Sedge Wren - Cistothorus stellaris
Plumage of the adult is warm and pale brown overall, giving the bird a "dull, plain-faced" appearance (Vickery 1983). The deep brown wing coverts and short tail are barred, the flanks are buff-orange, the chin, throat and center belly are dull white, and the undertail coverts are plain buff. The crown is "finely, somewhat obscurely, streaked with tan and dark brown" (Vickery 1983), and the tail is typically cocked over the back. The sexes have similar plumages, with males about a gram heavier than females (species weight ranges from 7 to 10 grams) (Taylor et al. 1983, Herkert et al. 2001). Juveniles are similar to adults except that the streaking is less conspicuous on the head and neck and more conspicuous on the back, with more of a buff coloration on the throat and abdomen than the adults (Forbush 1929, Walkinshaw 1935).
The song of males is a dry, staccato chattering "chap chap chap chapper-rrrrr
" (Peterson 1980). Among individuals, the song's introduction is stereotyped, whereas the trill is highly variable (Kroodsma and Verner 1978). The call note is "churr churr
," "chap churr
," or "chap
" (Bent 1948, Peterson 1980). Sedge Wrens frequently sing at night (Vickery 1983).
For a comprehensive review of the conservation status, habitat use, and ecology of this and other Montana bird species, please see Marks et al. 2016, Birds of Montana.
In contrast to the Marsh Wren (Cistothorus palustris), the other wren to occur primarily in wetlands, the Sedge Wren lacks a distinct white stripe over the eye, is lighter-colored, and has a shorter bill (Vickery 1983). The Sedge Wren's streaked crown, smaller size, and distinctive song distinguish it from the House Wren (Tryglodytes aedon) (Herkert et.al 2001).
Observations in Montana Natural Heritage Program Database
Number of Observations:
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Map Help and Descriptions
SUMMER (Feb 16 - Dec 14)
Direct Evidence of Breeding
Indirect Evidence of Breeding
No Evidence of Breeding
WINTER (Dec 15 - Feb 15)
Not Regularly Observed
(Observations spanning multiple months or years are excluded from time charts)
The migratory pattern of this species in Montana is poorly known, and few records exist for the state. The earliest recorded date for Sedge Wren in Montana occurred in April 1909 in Gallatin County. Two recent records for Westby and Fort Peck indicate the presence of individuals in May (Montana Bird Distribution Committee 2012). In 1979, a Sedge Wren was observed in Great Falls during the third week in September, the latest season date for the species in the state (Wright 1996, Montana Bird Distribution Committee 2012).
No specific information exists, but appropriate wetland habitat is present in the areas of the state in which the species has been recorded.
Ecological Systems Associated with this Species
- Details on Creation and Suggested Uses and Limitations
How Associations Were Made
We associated the use and habitat quality (common or occasional) of each of the 82 ecological systems mapped in Montana for
vertebrate animal species that regularly breed, overwinter, or migrate through the state by:
- Using personal observations and reviewing literature that summarize the breeding, overwintering, or migratory habitat requirements of each species (Dobkin 1992, Hart et al. 1998, Hutto and Young 1999, Maxell 2000, Foresman 2012, Adams 2003, and Werner et al. 2004);
- Evaluating structural characteristics and distribution of each ecological system relative to the species' range and habitat requirements;
- Examining the observation records for each species in the state-wide point observation database associated with each ecological system;
- Calculating the percentage of observations associated with each ecological system relative to the percent of Montana covered by each ecological system to get a measure of "observations versus availability of habitat".
Species that breed in Montana were only evaluated for breeding habitat use, species that only overwinter in Montana were only evaluated for overwintering habitat use, and species that only migrate through Montana were only evaluated for migratory habitat use.
In general, species were listed as associated with an ecological system if structural characteristics of used habitat documented in the literature were present in the ecological system or large numbers of point observations were associated with the ecological system.
However, species were not listed as associated with an ecological system if there was no support in the literature for use of structural characteristics in an ecological system, even if
point observations were associated with that system.
Common versus occasional association with an ecological system was assigned based on the degree to which the structural characteristics of an ecological system matched the preferred structural habitat characteristics for each species as represented in scientific literature.
The percentage of observations associated with each ecological system relative to the percent of Montana covered by each ecological system was also used to guide assignment of common versus occasional association.
If you have any questions or comments on species associations with ecological systems, please contact the Montana Natural Heritage Program's Senior Zoologist.
Suggested Uses and Limitations
Species associations with ecological systems should be used to generate potential lists of species that may occupy broader landscapes for the purposes of landscape-level planning.
These potential lists of species should not be used in place of documented occurrences of species (this information can be requested at: mtnhp.org/requests
) or systematic surveys for species and evaluations of habitat at a local site level by trained biologists.
Users of this information should be aware that the land cover data used to generate species associations is based on imagery from the late 1990s and early 2000s and was only intended to be used at broader landscape scales.
Land cover mapping accuracy is particularly problematic when the systems occur as small patches or where the land cover types have been altered over the past decade.
Thus, particular caution should be used when using the associations in assessments of smaller areas (e.g., evaluations of public land survey sections).
Finally, although a species may be associated with a particular ecological system within its known geographic range, portions of that ecological system may occur outside of the species' known geographic range.
- Adams, R.A. 2003. Bats of the Rocky Mountain West; natural history, ecology, and conservation. Boulder, CO: University Press of Colorado. 289 p.
- Dobkin, D. S. 1992. Neotropical migrant land birds in the Northern Rockies and Great Plains. USDA Forest Service, Northern Region. Publication No. R1-93-34. Missoula, MT.
- Foresman, K.R. 2012. Mammals of Montana. Second edition. Mountain Press Publishing, Missoula, Montana. 429 pp.
- Hart, M.M., W.A. Williams, P.C. Thornton, K.P. McLaughlin, C.M. Tobalske, B.A. Maxell, D.P. Hendricks, C.R. Peterson, and R.L. Redmond. 1998. Montana atlas of terrestrial vertebrates. Montana Cooperative Wildlife Research Unit, University of Montana, Missoula, MT. 1302 p.
- Hutto, R.L. and J.S. Young. 1999. Habitat relationships of landbirds in the Northern Region, USDA Forest Service, Rocky Mountain Research Station RMRS-GTR-32. 72 p.
- Maxell, B.A. 2000. Management of Montana's amphibians: a review of factors that may present a risk to population viability and accounts on the identification, distribution, taxonomy, habitat use, natural history, and the status and conservation of individual species. Report to U.S. Forest Service Region 1. Missoula, MT: Wildlife Biology Program, University of Montana. 161 p.
- Werner, J.K., B.A. Maxell, P. Hendricks, and D. Flath. 2004. Amphibians and reptiles of Montana. Missoula, MT: Mountain Press Publishing Company. 262 p.
No food habits data are available for Montana, but other studies indicate Sedge Wren diet consists mainly of spiders and insects. Ants, bugs, weevils, ladybird beetles, moths, caterpillars, locusts, crickets, and grasshoppers are, at times, also included (Howell 1932, Terres 1980). Prey is picked from the ground or from foliage. Walkinshaw (1935) observed the birds feeding their young moths, spiders, mosquitoes, flies, grasshoppers, and bugs. The "mouse-like," inconspicuous feeding behavior suggests that these birds forage mainly at ground level, probably for insects hiding in moist soil and among bases of sedges and grasses (Howell 1932, Walkinshaw 1935).
Sedge Wrens are adapted to foraging in shrubby grasslands, owing to their small size, relatively long bills, and longer legs in comparison to other wren species using forested habitats (Niemi 1985). Abundant insect food in upland habitats, probably a function of rainfall, soil moisture, and productivity of adjacent marshlands, often attracts Sedge Wrens to feed away from wetland habitat (Orians 1980).
No information is currently present regarding Sedge Wren ecology in Montana. It is known from other studies of Sedge Wren ecology that grazing has a negative effect on their ability to find appropriate habitat and the densities of nesting males decrease as areas are grazed (Walkinshaw 1935, Stewart and Robbins 1958, Cink and Sepahi 1983, Birkenholz 1984, Higgins et al. 1984, Hanowski and Niemi 1986, Manci and Rusch 1988, Lingle and Bedell 1989). Sedge Wrens may destroy the eggs of other Sedge Wrens or other small birds.
The average size of a Sedge Wren's nesting territory is about 0.2 hectare (Byrd and Johnston 1991). Estimates of territory size for five males in Minnesota averaged 1,280 meters squared (Burns 1982).
Preferred habitat are areas that are highly susceptible to flooding and drying caused by annual and seasonal variation in rainfall. Because their preferred habitat is so influenced by seasonal and annual changes in moisture, Sedge Wrens are relatively mobile in their selection of nesting sites and may be totally absent in some years from regions in which they previously nested (Kroodsma and Verner 1978, Cody 1985).
Vegetative succession and disturbance by grazing, haying, and planting also impart a highly transitory character to nesting habitats. This habitat instability may lead to the high mobility and low site tenacity of Sedge Wrens (Kroodsma and Verner 1978). The complete regional absence in some years, however, suggests that some factor in addition to habitat instability is involved in population fluctuations, perhaps regional patterns of rainfall or weather conditions during migration. The nature of the communication system as a unique adaptation to high population mobility (Kroodsma and Verner 1978) suggests that opportunistic breeding and low site tenacity has occurred for a long time, rather than being of recent origin, such as in response to agriculture and habitat loss (Burns 1982). These birds are "curiously local" and occur sporadically within the Andean Zone of South America, and there is no reason to believe that anthropogenic factors influence the species' distribution there (Fjeldsa 1988).
Information on species reproduction is unavailable for the state as no records exist containing direct evidence of breeding. A territorial pair was observed and recorded in Westby in 1988 and 1996 (Wright 1996), and behavior observed on several other occasions in Westby and Medicine Lake suggests breeding (Wright 1996, Montana Bird Distribution Committee 2012). Reproduction information from studies elsewhere record nests of Sedge Wrens being well-hidden, rounded balls made of woven, fine grasses and culms of sedges, typically with a single side entrance. They are often built near the ground (less than 0.5 m) and are attached to live stems of grasses and sedges (Walkinshaw 1935, Tordoff and Young 1951, Harrison 1987).
Sedge Wren eggs are ovate or pointed-ovate, white and unmarked, smooth and moderately glossy (Harrison 1987), and measure approximately 16 by 12 mm (Bent 1948).
Nesting phenology may be related to site latitude and often occurs in two "waves" during a given season. Sedge Wrens arrive at nesting areas as early as mid-April (Bent 1948) in some regions or as late as July in others (Lingle and Bedell 1989), and have been observed nesting as late as the end of September (Schwilling 1982). Nesting in many northeastern states, especially in the more northerly latitudes, may be initiated from May to June, but may not occur until as late as July (Lingle and Bedell 1989). Late nesting at certain sites could represent renesting attempts by birds arriving from elsewhere or could be an adaptive response of local birds to delayed availability of moist, but unflooded, grassland habitats. Peak nesting populations in mixed-grass prairie in North Dakota occurred after unusually wet springs, but nesting activity showed little response to spring temperature (Cody 1985). Occupancy of a given site varies among years, and sites used one year may be abandoned the next (Palmer 1949, Burns 1982).
Upon arrival at nesting areas, males establish territories for courtship, nesting, and foraging (Burns 1982). Territory boundaries are fluid throughout the nesting season, and males may shift their activity and defend new areas as the season progresses. Males defend territories and attract mates by singing vigorously throughout the breeding season, as much as 22 h/day and at rates of up to 12 to 15 songs per minute (Walkinshaw 1935, Kroodsma and Verner 1978). This combination of song components may permit mixing of highly dispersive populations (Kroodsma and Verner 1978) and may represent an evolutionary compromise between species identification and sexual selection among individuals. Because local dialects would be swamped in such highly mobile populations, neighboring males do not share song-type repertoires nor do they counter-sing by matching song-types, as does Marsh Wren.
Males build multiple, domed nests that figure prominently in courtship, and may also serve as dormitories and decoys for predators (Verner 1965, Picman and Picman 1980, Burns 1982). In Minnesota, males built an average of 7.4 complete nests and 0.8 incomplete nests on each territory (Burns 1982). Nests used for incubating eggs are built closer to the ground than dummy nests and have a substantial inner lining of grass, sedge, and feathers added by the female (Walkinshaw 1935, Burns 1982).
Females begin laying one egg daily about the third day of nest lining (Burns 1982), and initiate incubation before the clutch is complete. Usually 7 eggs are laid per clutch (range is 2 to 8), although clutches laid later in the season may be smaller (Bent 1948, Harrison 1978, Burns 1982). A clutch of 4 eggs is average in Costa Rica (Stiles and Skutch 2003). Incubation is by the female only and lasts about 14 days (Burns 1982).
Females in some populations are double-brooded, but are single-brooded in others (Walkinshaw 1935, Crawford 1977, Burns 1982). Males may be serially or simultaneously polygynous and females may be serially polyandrous (Crawford 1977, Burns 1982). Mates of monogamous males had higher reproductive success than both primary and secondary females mated with polygynous males, whereas polygynous males had higher reproductive success than monogamous males (Burns 1982).
Nest success (nests with at least one egg hatching) was reported at 68% (n = 31 nests, Crawford 1977) and 69% (n = 18 nests, Burns 1982). Sources of nest loss include predation, infertile clutches, heavy rains, trampling by grazing cattle, and nest destruction by other Sedge Wrens (Walkinshaw 1935, Crawford 1977, Picman and Picman 1980, Burns 1982). The nestling period lasts 13 to 14 days (Walkinshaw 1935, Crawford 1977). Fledging success (number of young fledged per number of eggs laid) has been reported at 0.67 in Minnesota (Burns 1982). The female provides virtually all parental care of nestlings, although males occasionally feed nestlings (Walkinshaw 1935, Burns 1982). Nest-building and continual defense by males of territories with abundant food may compensate females for a lack of male parental care of offspring. Fledglings move about in small groups until migration occurs (Gibbs and Melvin 1992).
No known active management is ongoing for Sedge Wren in the state. Sedge Wrens are a Species of Management Concern in U.S. Fish and Wildlife Service Region 6 (USFWS 1995).
- Literature Cited AboveLegend: View Online Publication
- Bent, A. C. 1948. Life histories of North American nuthatches, wrens, thrashers, and their allies. U.S. National Museum Bulletin No. 195.
- Birkenholz, D. 1984. Restored tall grass prairie. American Birds 38:96.
- Burns, J.T. 1982. Nests, territories, and reproduction of sedge wrens (Cistothorus platensis). Wilson Bulletin 94(3):338- 349.
- Byrd, M.A. and D.W. Johnston. 1991. Birds. In: K. Terwilliger, coord. Virginia's endangered species: proceedings of a symposium. p. 477-537. McDonald and Woodward Publishing Company, Blacksburg, Virginia.
- Cink, C. and P. Sepahi. 1983. Floodplain tall grass prairie. American Birds 37:83.
- Cody, M. L. 1985. Habitat selection in grassland and open-country birds. In: M. L. Cody ed. p. 191-226. Habitat selection in birds. Academic Press, Orlando, Florida. 558 pp.
- Crawford, R.D. 1977. Polygynous breeding of short-billed marsh wrens. Auk 94:359-362.
- Fjeldsa, J. 1988. Status of birds in steppe habitats of the Andean Zone and Patagonia. In: P.D. Goriup, ed. p. 81-95. International Council for Bird Preservation Technical Publication Number 7. 250 pp.
- Forbush, E. H. 1929. Birds of Massachusetts and other New England states. 3 volumes. Massachusetts Department of Agriculture, Boston.
- Gibbs, J. P. and S. M. Melvin. 1992. Sedge wren, Cistothorus platensis. In: K. J. Schneider and D. M. Pence, eds. Migratory nongame birds of management concern in the Northeast. p. 191-209 U.S. Fish and Wildlife Service, Newton Corner, Massachusetts. 400 pp.
- Hanowski, J. M. and G. J. Niemi. 1986. Habitat characteristics for bird species of special concern. Minnesota Department of Natural Resources, St. Paul, Minnesota. Unpublished report.
- Harrison, C.J.O. 1978. A field guide to the nests, eggs and nestlings of North American birds. Collins, Cleveland.
- Higgins, K. F., T. W. Arnold, and R. M. Barta. 1984. Breeding bird community colonization of sown stands of native grasses in North Dakota. Prairie Naturalist 16:177-182.
- Howell, A. H. 1932. Florida bird life. Coward-McCann, New York. 579 pp.
- Kroodsma, D.E. and J. Verner. 1978. Complex singing behaviors among Cistothorus wrens. Auk 95:703-716.
- Lingle, G.R. and P.A. Bedell. 1989. Nesting ecology of sedge wrens in Hall County, Nebraska. Nebraska Bird Review 56:47-49.
- Manci, K. M. and D. H. Rusch. 1988. Indices to distribution and abundance of some inconspicuous waterbirds at Horicon Marsh. Journal of Field Ornithology 59:67-75.
- Marks, J.S., P. Hendricks, and D. Casey. 2016. Birds of Montana. Arrington, VA. Buteo Books. 659 pages.
- Montana Bird Distribution Committee. 2012. P.D. Skaar's Montana bird distribution. 7th Edition. Montana Audubon, Helena, Montana. 208 pp. + foldout map.
- Niemi, G. J. 1985. Patterns of morphological evolution in bird genera of New World and Old World peatlands. Ecology 66:1215-1228.
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- Picman, J. and A.K. Picman. 1980. Destruction of nests by the short-billed marsh wren. Condor 82:176-179.
- Schwilling, M.D. 1982. Sedge wrens nesting into September. Kansas Ornithological Society Bulletin 33:22-23.
- Stewart, R. E. and C. S. Robbins. 1958. Birds of Maryland and the District of Columbia. North American Fauna Number 62. U.S. Government Printing Office, Washington, D.C.
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- U.S. Fish and Wildlife Service, Office of Migratory Bird Management. 1995. Migratory nongame birds of management concern in the United States: the 1995 list. U.S. Government Printing Office: 1996-404-911/44014. 22 pp.
- Verner, J. 1965. Breeding biology of the long-billed marsh wren. Condor 67:6-30.
- Vickery, P. 1983. Sedge wren. In: J. Farrand, ed. The Audubon Society master guide to birding, Volume 2:352-354. Alfred A. Knopf, New York, New York. 398 pp.
- Walkinshaw, L. R. 1935. Studies of the short-billed marsh wren (Cistothorus stellaris) in Michigan. Wilson Bulletin 52:361-368.
- Wright, P.L. 1996. Status of rare birds in Montana, with comments on known hybrids. Northwestern Naturalist 77(3):57-85.
- Additional ReferencesLegend: View Online Publication
Do you know of a citation we're missing?
- American Ornithologists Union. 1983. Checklist of North American birds, 6th Edition. 877 PP.
- American Ornithologists’ Union [AOU]. 1998. Check-list of North American birds, 7th edition. American Ornithologists’ Union, Washington, D.C. 829 p.
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- Bent, A. C. 1949. Life histories of North American thrushes, kinglets, and their allies. U.S. National Museum Bulletin No. 196. 452 p.
- Bird Conservancy of the Rockies. 2017. Pocket Guide to Northern Prairie Birds. Brighton, CO: Bird Conservancy of the Rockies. 98 p.
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- Crawford, R. L. 1981. Bird kills at a lighted man-made structure: often on nights close to a full moon. Am. Birds 35(6):913-914.
- Dobkin, D. S. 1992. Neotropical migrant landbirds in the Northern Rockies and Great Plains. U.S.D.A. For. Serv. N. Region Publ. R1-93-34. Missoula, Mont.
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- Hays, R., R.L. Eng, and C.V. Davis (preparers). 1984. A list of Montana birds. Helena, MT: MT Dept. of Fish, Wildlife & Parks.
- Herkert, J.R., D.E. Kroodsma, and J.P. Gibbs. 2001. Sedge Wren (Cistothorus platensis). Species Account Number 582. The Birds of North America Online (A. Poole, Ed.). Ithaca, NY: Cornell Laboratory of Ornithology; Retrieved 3/25/2008 from The Birds of North America Online database
- Hilty, S. L., and W. L. Brown. 1986. A guide to the birds of Colombia. Princeton University Press, Princeton, New Jersey. 836 pp.
- Jalava, J. 1993. Status Report on the Sedge Wren Cistothorus platensis stellaris (Naumann) in Canada. Committee On the Status of Endangered Wildlife in Canada (COSEWIC), Ottawa, ON. 50 pp.
- Lenard, S., J. Carlson, J. Ellis, C. Jones, and C. Tilly. 2003. P. D. Skaar's Montana bird distribution, 6th edition. Montana Audubon, Helena, MT. 144 pp.
- Niemi, G. J., and J. M. Hanowski. 1984. Effects of a transmission line on bird populations in the Red Lake peatland, northern Minnesota. Auk 101:487-498.
- Noyes, G. H. 1941. New England section. U.S. Weather Bureau, Climatological Data 52(13)73-77.
- Pavlacky Jr., D.C., et al. 2021. Landscape-scale conservation mitigates the biodiversity loss of grassland birds. Ecological Applications e2548. 17 p.
- Root, T. L. 1988. Atlas of wintering North American birds: An analysis of Christmas Bird Count data. University of Chicago Press, Chicago. 312 pp.
- Sibley, D. 2014. The Sibley guide to birds. Alfred A. Knopf, New York, NY. 598 pp.
- Skaar, P.D. 1969. Birds of the Bozeman latilong: a compilation of data concerning the birds which occur between 45 and 46 N. latitude and 111 and 112 W. longitude, with current lists for Idaho, Montana, Wyoming, impinging Montana counties and Yellowstone National Park. Bozeman, MT. 132 p.
- Tate, J., and D. J. Tate. 1982. The blue list for 1982. Am. Birds 36:126-135.
- Tiner, R. W., Jr. 1984. Wetlands of the United States: current status and recent trends. U.S. Fish and Wildlife Service, National Wetlands Inventory, Washington, D.C. 59 pp.
- U.S. Forest Service. 1991. Forest and rangeland birds of the United States: Natural history and habitat use. U.S. Department of Agriculture, Forest Service Agricultural Handbook 688. 625 pages.
- Warren, B. H. 1890. Report on the birds of Pennsylvania. 2nd Edition. Pennsylvania State Boad Agric., Harrisburg, Pennsylvania. 434 pp.
- Additional Sources of Information Related to "Birds"