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Check-list of North American birds. Seventh edition. American Ornithologists' Union, Washington, D.C. [as modified by subsequent supplements and corrections published in <i>The Auk</i>]. 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Be cautious about creating EOs for observations that may represent single breeding events outside the normal breeding distribution.","mappingGuidance":"Breeding occurrences include nesting areas as well as foraging areas.<br/><br/>For swallows and other species that have separate nesting and foraging areas, separations are based on nest sites or nesting areas, not to locations of foraging individuals. For example, nesting areas separated by a gap larger than the separation distance are different occurrences, regardless of the foraging locations of individuals from those nesting areas. This separation procedure is appropriate because nesting areas are the critical aspect of swallow breeding occurrences, tend to be relatively stable or at least somewhat predictable in general location, and so are the basis for effective conservation; foraging areas are much more flexible and not necessarily static.","separationBarriers":null,"separationDistanceUnsuitableHabitatat":5.0,"separationDistanceSuitableHabitatat":5.0,"altSeparationProcedure":null,"separationJustification":"Significant dispersal and associated high potential for gene flow among populations of birds separated by tens of kilometers (e.g., Moore and Dolbeer 1989), and increasing evidence that individuals leave their usual home range to engage in extrapair copulations, as well as long foraging excursions of some species, make it difficult to circumscribe occurrences on the basis of meaningful population units without occurrences becoming too large. Hence, a moderate, standardized separation distance has been adopted for songbirds and flycatchers; it should yield occurrences that are not too spatially expansive while also accounting for the likelihood of gene flow among populations within a few kilometers of each other.<br/><br/>Be careful not to separate a population's nesting areas and foraging areas as different occurrences; include them in the same occurrence even if they are more than 5 km apart. Mean foraging radius (from nesting area) of Brown-headed Cowbird females was 4.0 kilometers in California, 1.2 kilometers in Illinois-Missouri (Thompson 1994). Yellow-headed Blackbirds, Brewer's Blackbirds, and probably Red-winged Blackbirds all forage up to 1.6 kilometers away from breeding colony (Willson 1966, Horn 1968). In one study, Brewer's Blackbirds were found as far as 10 kilometers from nesting area (Williams 1952), but this may be unusual.<br/><br/>For swallows and other passerines with similar behavioral ecology, separation distance pertains to nest sites or nesting colonies, not to locations of foraging individuals. For example, nesting areas separated by a gap of more than 5 km are different occurrences, regardless of the foraging locations of individuals from those nesting areas. This separation procedure is appropriate because nesting areas are the critical aspect of swallow breeding occurrences, tend to be relatively stable or at least somewhat predictable in general location, and so are the basis for effective conservation; foraging areas are much more flexible and not necessarily static.<br/><br/>Be cautious about creating EOs for observations that may represent single breeding events outside the normal breeding distribution.<br/><br/>Unsuitable habitat: Habitat not normally used for breeding/feeding by a particular species. For example, unsuitable habitat for grassland and shrubland birds includes forest/woodland, urban/suburban, and aquatic habitats. Most habitats would be suitable for birds with versatile foraging habits (e.g., most corvids).","versionDate":"2004-09-10","versionAuthor":"Hammerson, G.","versionNotes":null,"lastModified":"2025-12-05T22:48:36.225047Z"},{"eoSpecsDetailId":124588,"locationUseClass":{"id":3,"locationUseClassDescEn":"Nonbreeding","locationUseClassDescEs":"No reproducción","locationUseClassDescFr":"Non-reproduction","displayOrder":3},"eoSpecGroupName":"Passerines","subtypes":"Foraging Area, Roost Site","inferredExtentDistance":null,"inferredExtentNotes":null,"minimumEoCriteria":"Any area used traditionally in the nonbreeding season (used for populations that are not resident in a location year-round). Minimally, reliable observations of 10 or more individuals in appropriate habitat for 20 or more days at a time. For G1-G3 species, observations of fewer individuals could constitute an occurrence of conservation value. Sites used during migration should be documented under the 'migratory stopover' location use class.","mappingGuidance":null,"separationBarriers":null,"separationDistanceUnsuitableHabitatat":5.0,"separationDistanceSuitableHabitatat":5.0,"altSeparationProcedure":null,"separationJustification":"Separation distance is necessarily arbitrary but attempts to balance the high mobility of birds with the need for occurrences of reasonable spatial scope. Note that a population's roost sites and foraging areas are parts of the same occurrence, even if they are more than 5 km apart.<br/><br/>For swallows and other species with similar behavioral ecology, the separation distance pertains to communal roost sites rather than to foraging areas; the former tend to be more stable and specific over time than the latter.","versionDate":"2004-09-03","versionAuthor":"Hammerson, G.","versionNotes":null,"lastModified":"2025-12-05T22:48:36.225047Z"},{"eoSpecsDetailId":124589,"locationUseClass":{"id":4,"locationUseClassDescEn":"Migratory stopover","locationUseClassDescEs":"Parada migratoria","locationUseClassDescFr":"Halte migratoire","displayOrder":5},"eoSpecGroupName":"Passerines","subtypes":"Foraging Area, Roost Site","inferredExtentDistance":null,"inferredExtentNotes":null,"minimumEoCriteria":"For most passerines: Evidence of recurring presence of migrating individuals (including historical) and potential recurring presence at a given location; minimally a reliable observation of 25 birds in appropriate habitat.<br/><br/>For swallows: Evidence of recurring presence of migrating flocks (including historical) and potential recurring presence at a given location; minimally a reliable observation of 100 birds in appropriate habitat (e.g., traditional roost sites).<br/><br/>Occurrences should be locations where the species is resident for some time during the appropriate season; it is preferable to have observations documenting presence over at least 7 days annually.<br/><br/>EOs should not be described for species that are nomadic during nonbreeding season: e.g., Lark Bunting.<br/><br/>Be cautious about creating EOs for observations that may represent single events.","mappingGuidance":null,"separationBarriers":null,"separationDistanceUnsuitableHabitatat":5.0,"separationDistanceSuitableHabitatat":5.0,"altSeparationProcedure":null,"separationJustification":"Separation distance somewhat arbitrary but intended to define occurrences of manageable size for conservation purposes. Occurrences defined primarily on the basis of areas supporting concentrations of birds, rather than on the basis of distinct populations.<br/><br/>For swallows and other species with similar behavioral ecology, the separation distance pertains to communal roost sites rather than to foraging areas; the former tend to be more stable and specific over time than the latter.","versionDate":"2004-09-03","versionAuthor":"Hammerson, G., and S. Cannings","versionNotes":null,"lastModified":"2025-12-05T22:48:36.225047Z"},{"eoSpecsDetailId":124586,"locationUseClass":{"id":13,"locationUseClassDescEn":"Nonmigratory","locationUseClassDescEs":"No migratorio","locationUseClassDescFr":"Non migratrice","displayOrder":20},"eoSpecGroupName":"Passerines","subtypes":null,"inferredExtentDistance":null,"inferredExtentNotes":null,"minimumEoCriteria":"Occurrences are based on evidence of historical presence, or current and likely recurring presence, at a particular location. Such evidence minimally includes collection or reliable observation and documentation of one or more individuals in or near appropriate habitat.<br/><br/>These occurrence specifications are used for nonmigratory populations of passerine birds.","mappingGuidance":null,"separationBarriers":"None.","separationDistanceUnsuitableHabitatat":5.0,"separationDistanceSuitableHabitatat":5.0,"altSeparationProcedure":null,"separationJustification":"Significant dispersal and associated high potential for gene flow among populations of birds separated by tens of kilometers (e.g., Moore and Dolbeer 1989), and increasing evidence that individuals leave their usual home range to engage in extrapair copulations, as well as long foraging excursions of some species, make it difficult to circumscribe occurrences on the basis of meaningful population units without occurrences becoming too large. Hence, a moderate, standardized separation distance has been adopted for songbirds and flycatchers; it should yield occurrences that are not too spatially expansive while also accounting for the likelihood of gene flow among populations within a few kilometers of each other.<br/><br/>Be careful not to separate a population's nesting areas and breeding-season foraging areas as different occurrences; include them in the same occurrence even if they are more than 5 km apart. Blue jays have small summer home ranges but fly up to 4 kilometers to harvest mast (Tarvin and Woolfenden 1999). Flocks of pinyon jays range over 21-29 square kilometers (Ligon 1971, Balda and Bateman 1971); nesting and foraging areas may be widely separated. Tricolored blackbirds forage in flocks that range widely to more than 15 kilometers from the nesting colony (Beedy and Hamilton 1999).<br/><br/>Unsuitable habitat: Habitat not normally used for breeding/feeding by a particular species. For example, unsuitable habitat for grassland and shrubland birds includes forest/woodland, urban/suburban, and aquatic habitats. Most habitats would be suitable for birds with versatile foraging habits (e.g., most corvids).","versionDate":"2004-09-10","versionAuthor":"Hammerson, G.","versionNotes":"These specs pertain to nonmigratory species.","lastModified":"2025-12-05T22:48:36.225047Z"}],"plantCharacteristics":null,"elementManagement":{"elementGlobalId":104831,"eoManagementGroupName":null,"stewardshipOverview":null,"impacts":null,"restorationPotential":null,"siteConservationPlansConsidered":null,"managementMethods":null,"monitoringMethods":null,"managementProgramContacts":null,"monitoringProgramContacts":null,"managementResearchPrograms":null,"managementResearchNeeds":null,"biologicalResearchNeeds":null,"additionalTopics":null},"occurrenceViabilities":[{"eoRankSpecsDetailId":106273,"eoRankSpecsGroupName":null,"locationUseClass":{"id":1,"locationUseClassDescEn":"Not applicable","locationUseClassDescEs":"No se aplica","locationUseClassDescFr":"Sans objet","displayOrder":1},"excellentViability":null,"goodViability":null,"fairViability":null,"poorViability":null,"viabilityJustification":"Use the Generic Guidelines for the Application of Occurrence Ranks (2008).<br>The Key for Ranking Species Occurrences Using the Generic Approach provides a step-wise process for implementing this method.","versionDate":null,"versionAuthor":null,"versionNotes":null,"lastModified":"2020-05-14T02:27:35.183013Z"}],"references":[{"id":153779,"citation":"American Ornithologists' Union (AOU). 1983. 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Also available online: http://www.aou.org/.","shortCitationAuthor":"American Ornithologists' Union (AOU)","shortCitationYear":1998,"referenceCode":"B98AOU01NAUS","lastModified":"2020-02-25T14:38:12.673494Z"},{"id":765524,"citation":"American Ornithologists' Union (AOU). Chesser, R.T., K.J. Burns, C. Cicero, J.L. Dunn, A.W. Kratter, I.J. Lovette, P.C. Rasmussen, J.V. Remsen, Jr., J.D. Rising, D.F. Stotz, and K. Winker. 2016. Fifty-seventh Supplement to the American Ornithologists' Union Check-list of North American Birds. The Auk 133:544-560.","shortCitationAuthor":"American Ornithologists' Union (AOU)","shortCitationYear":2016,"referenceCode":"A16AOU01EHUS","lastModified":"2020-02-25T18:12:15.272707Z"},{"id":115080,"citation":"Balda, R. P., and G. C. Bateman. 1971. Flocking and annual cycle of the piñon jay, <i>Gymnorhinus cyanocephalus</i>. Condor 73:287-302.","shortCitationAuthor":"Balda and Bateman","shortCitationYear":1971,"referenceCode":"A71BAL01NACA","lastModified":"2020-02-25T14:38:12.657866Z"},{"id":792472,"citation":"Dickinson, E.C., and L. Christidis (eds.). 2014. The Howard and Moore complete checklist of the birds of the world, 4th ed., Volume 2: Passerines. Aves Press, Eastbourne, U.K. 752 pp.","shortCitationAuthor":"Dickinson and Christidis","shortCitationYear":2014,"referenceCode":"B14DIC01NAUS","lastModified":"2020-02-25T18:20:22.67091Z"},{"id":792474,"citation":"Gill, F., and D. Donsker (eds.). 2016. IOC World Bird List, version 6.1. Available online at http://www.worldbirdnames.org/.","shortCitationAuthor":"Gill and Donsker","shortCitationYear":2016,"referenceCode":"W16GIL01NAUS","lastModified":"2020-02-25T18:20:22.67091Z"},{"id":103790,"citation":"Godfrey, W.E. 1966. The birds of Canada. National Museums of Canada. Ottawa. 428 pp.","shortCitationAuthor":"Godfrey","shortCitationYear":1966,"referenceCode":"B66GOD01NAUS","lastModified":"2020-02-25T14:38:14.361032Z"},{"id":100210,"citation":"Harrison, C. 1978. A Field Guide to the Nests, Eggs and Nestlings of North American Birds. Collins, Cleveland, Ohio.","shortCitationAuthor":"Harrison","shortCitationYear":1978,"referenceCode":"B78HAR01NAUS","lastModified":"2020-02-25T14:38:12.657866Z"},{"id":105464,"citation":"Horn, H. S. 1968. The adaptive significance of colonial nesting in the Brewer's Blackbird. Ecology 49:682-694.","shortCitationAuthor":"Horn","shortCitationYear":1968,"referenceCode":"A68HOR01NACA","lastModified":"2020-02-25T14:38:12.689104Z"},{"id":144453,"citation":"Ligon, J. D. 1971. Late summer-autumnal breeding of the piñon jay in New Mexico. Condor 73:147-153.","shortCitationAuthor":"Ligon","shortCitationYear":1971,"referenceCode":"A71LIG01NACA","lastModified":"2020-02-25T14:38:12.704742Z"},{"id":115752,"citation":"Moore, W. S., and R. A. Dolbeer. 1989. The use of banding recovery data to estimate dispersal rates and gene flow in avian species: case studies in the Red-winged Blackbird and Common Grackle. Condor 91:242-253.","shortCitationAuthor":"Moore and Dolbeer","shortCitationYear":1989,"referenceCode":"A89MOO01NACA","lastModified":"2020-02-25T14:38:12.657866Z"},{"id":158711,"citation":"Poole, A. F. and F. B. Gill. 1992. The birds of North America. The American Ornithologists' Union, Washington, D.C. and The Academy of Natural Sciences, Philadelphia, PA.","shortCitationAuthor":"Poole and Gill","shortCitationYear":1992,"referenceCode":"B92POO0100LA","lastModified":"2020-02-25T14:38:12.673494Z"},{"id":110252,"citation":"Pough, R. H. 1957. Audubon Western Bird Guide. Doubleday. 316 pp.","shortCitationAuthor":"Pough","shortCitationYear":1957,"referenceCode":"B57POU01NAUS","lastModified":"2020-02-25T18:13:57.290075Z"},{"id":122670,"citation":"Pratt, H. D., P. L. Bruner, and D. G. Berrett. 1987. A Field Guide to the Birds of Hawaii and the Tropical Pacific. Princeton University Press, Princeton, New Jersey. 409 pp. + 45 plates.","shortCitationAuthor":"Pratt et al.","shortCitationYear":1987,"referenceCode":"B87PRA01NAUS","lastModified":"2020-02-25T14:38:18.8767Z"},{"id":146621,"citation":"Tarvin, K. A., and G. E. Woolfenden. 1999. Blue Jay (<i>Cyanocitta cristata</i>). No. 469 IN A. Poole and F. Gill, editors. The birds of North America. The Birds of North America, Inc., Philadelphia, PA. 32pp.","shortCitationAuthor":"Tarvin and Woolfenden","shortCitationYear":1999,"referenceCode":"A99TAR01NACA","lastModified":"2020-02-25T14:38:12.657866Z"},{"id":148565,"citation":"Terres, J. K. 1980. The Audubon Society encyclopedia of North American birds. Alfred A. Knopf, New York.","shortCitationAuthor":"Terres","shortCitationYear":1980,"referenceCode":"B80TER01NAUS","lastModified":"2020-02-25T14:38:12.657866Z"},{"id":106130,"citation":"Thompson, F. R., III. 1994. 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Incubation 11-12 days, by female. Nestlings altricial and downy, tended by both adults, leave nest about 9-10 days after hatching, may not fly until about 21 days old (Terres 1980).","ecologyComments":"During winter, gathers into feeding flocks that may include > 100 individuals.","habitatComments":"Open country, grasslands, tundra, marshy and sandy areas, and wide forest clearings (AOU 1983). BREEDING: Nests in a shallow depression on the ground, lined with roots, grasses, and hair.","generalDescription":null,"diagnosticCharacteristics":null,"speciesMarineHabitats":[],"speciesTerrestrialHabitats":[{"cagTerrHabId":-111371,"terrestrialHabitat":{"id":9,"terrestrialHabitatDescEn":"Grassland/herbaceous","terrestrialHabitatDescEs":"Pastizales/cobertura herbácea","terrestrialHabitatDescFr":"Prairie/couverture herbacée","displayOrder":11}},{"cagTerrHabId":-111372,"terrestrialHabitat":{"id":13,"terrestrialHabitatDescEn":"Tundra","terrestrialHabitatDescEs":"Tundra","terrestrialHabitatDescFr":"Toundra","displayOrder":15}},{"cagTerrHabId":-111373,"terrestrialHabitat":{"id":19,"terrestrialHabitatDescEn":"Cropland/hedgerow","terrestrialHabitatDescEs":"Tierras cultivadas/cerco vivo","terrestrialHabitatDescFr":"Terre cultivée/haie","displayOrder":22}}],"speciesRiverineHabitats":[],"speciesPalustrineHabitats":[{"cagPalusHabId":-103284,"palustrineHabitat":{"id":2,"palustrineHabitatDescEn":"HERBACEOUS WETLAND","palustrineHabitatDescEs":"HUMEDAL HERBÁCEO","palustrineHabitatDescFr":"TERRE HUMIDE HERBACÉE","displayOrder":2}}],"speciesLacustrineHabitats":[],"speciesSubterraneanHabitats":[],"speciesEstuarineHabitats":[]},"primaryReference":{"id":765524,"citation":"American Ornithologists' Union (AOU). Chesser, R.T., K.J. Burns, C. Cicero, J.L. Dunn, A.W. Kratter, I.J. Lovette, P.C. Rasmussen, J.V. Remsen, Jr., J.D. Rising, D.F. Stotz, and K. Winker. 2016. Fifty-seventh Supplement to the American Ornithologists' Union Check-list of North American Birds. The Auk 133:544-560.","shortCitationAuthor":"American Ornithologists' Union (AOU)","shortCitationYear":2016,"referenceCode":"A16AOU01EHUS","lastModified":"2020-02-25T18:12:15.272707Z"},"predecessors":[],"elementGlobalThreatAssessments":[]}