Index of Species Information

WILDLIFE SPECIES:  Aphelocoma coerulescens


Introductory

WILDLIFE SPECIES: Aphelocoma coerulescens
AUTHORSHIP AND CITATION : Snyder, S. A. 1992. Aphelocoma coerullescens. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/ [].

ABBREVIATION : APCO COMMON NAMES : Florida scrub-jay scrub-jay TAXONOMY : The currently accepted scientific name for the Florida scrub-jay is Aphelocoma coerulescens (Bosc) [1,3]. ORDER : Passeriformes CLASS : Bird FEDERAL LEGAL STATUS : See OTHER STATUS OTHER STATUS : The Florida scrub-jay is federally [26] and state- [25] listed as threatened [24].

WILDLIFE DISTRIBUTION AND OCCURRENCE

WILDLIFE SPECIES: Aphelocoma coerulescens
GENERAL DISTRIBUTION : The Florida scrub-jay is restricted to the Florida Panhandle and central Florida. The two major populations are at Cape Canaveral/Merritt Island and the Ocala National Forest, Florida [9]. ECOSYSTEMS : FRES12 Longleaf-slash pine FRES13 Loblolly-shortleaf pine STATES :
FL

BLM PHYSIOGRAPHIC REGIONS : None KUCHLER PLANT ASSOCIATIONS : K112 Southern mixed forest
K113 Southern floodplain forest SAF COVER TYPES : 71 Longleaf pine-scrub oak 72 Southern scrub oak 73 Southern redcedar 74 Cabbage palmetto 75 Shortleaf pine 80 Loblolly pine-shortleaf pine 81 Loblolly pine SRM (RANGELAND) COVER TYPES : None PLANT COMMUNITIES : The Florida scrub-jay lives in sand pine (Pinus clausa) communities with bluestem (Andropogon floridanus) and panic grass (Panicum patentifolium) understories.  The scrub-jay also inhabits the xeric oak communities of Florida.  These communities include myrtle oak (Quercus myrtifolia), Chapman oak (Q. chapmanii), and sand live oak (Q. virginiana geminata) [21]. 

BIOLOGICAL DATA AND HABITAT REQUIREMENTS

WILDLIFE SPECIES: Aphelocoma coerulescens
TIMING OF MAJOR LIFE HISTORY EVENTS : Courtship - As early as January; build communal nests shortly after, from February to June; mate for life Clutch - lay three to five eggs between March and July; will lay one successful clutch per season; 17 days incubation Maturation - 1 year, but young birds remain with parents for an average of 2 years (up to 5 years) to help raise subsequent clutches Lifespan - average of 4.5 years; may live up to 11 years [9,18,21,23] PREFERRED HABITAT : Florida scrub-jays prefer dense thickets of sand pine scrub, oak flatwoods, recently burned sites, and shore dune thickets. Thickets, however, must have many open, sandy places for birds to feed [21]. Florida scrub-jays will build nests in myrtle oak, Chapman oak, and scrub palmetto (Serenoa spp.) but not in dense sand pine. Florida scrub jay populations are usually higher in oak cover between 3 and 6 feet (1-3 m) high. They will decrease in number with an increase in grass cover and woody cover (other than oak) that is less than 3 feet (1 m) high [9]. Scrub-jays tend to build their nests within 1.5 to 7.5 feet (0.5-2.5 m) of the ground [23]. COVER REQUIREMENTS : Florida scrub-jays nest in low, dense thickets of oak or wax myrtle (Myrica cerifera) [21,23]; some thickets, however, may be too dense for nesting. These thickets must be interspersed with sandy openings for feeding. Florida scrub-jays rarely use habitats with greater than 50 percent canopy cover [9]. Optimum habitat has been listed as oaks 1.5 to 6 feet (1-3 m) high covering 50 to 75 percent of the home range, interspersed with bare ground or vegetation less than 5.9 inches (15 cm) high covering 10 to 30 percent of the home range [9]. FOOD HABITS : Florida scrub-jays eat a variety of foods from grains, acorns, fruits, and nuts to frogs, lizards, arthropods, moths, bees, spiders, turtles, and mice [2,9,10,18,20]. PREDATORS : The biggest threat to the Florida scrub-jay is habitat destruction by man [9]. Predators include many species of snake, crows, magpies, and other jays (Corvids), bobcat (Felis rufus), and the grey fox (Urocyon cinereoargenteus) [21]. MANAGEMENT CONSIDERATIONS : The Florida scrub-jay does not disperse far from where it hatches. This can lead to habitat saturation, where no available nesting space opens for young breeding birds. Habitat destruction, by the birds themselves, can result from this overcrowding [9,21]. Clearcut sand pine stands in Florida tend to recover faster than burned stands; thus, Florida scrub-jays can recolonize clearcut stands more quickly than burned stands [9].

FIRE EFFECTS AND USE

WILDLIFE SPECIES: Aphelocoma coerulescens
DIRECT FIRE EFFECTS ON ANIMALS : Fires during the nesting season may destroy Florida scrub-jay nests. HABITAT RELATED FIRE EFFECTS : Fire-destroyed habitat can force Florida scrub-jays to relocate their home ranges temporarily [21]. However, scrub oaks, when burned, are quick to resprout, and usually are not replaced by southern pines, which may be unsuitable for Florida scrub-jay habitat [9]. Fire exclusion from Florida scrub-jay habitat allows sand pine and other species to become too dense for bird populations [9]. Too frequent fires can also kill oaks, which are needed for food and shelter [5]. Fires on the Merritt Island National Wildlife Refuge, Florida, also did not benefit scrub-jay populations [6]. The authors suggested that area sample sizes may have biased this conclusion. Florida scrub-jay populations did not show a significant increase following a late November prescribed fire in oak/palmetto palm scrub in central Florida [5]. Florida scrub-jay densities were higher in the mechanically cleared oak scrub types than in the burned oak/palmetto types. However, the beneficial effects of fire for scrub-jays may take a long time to become apparent; Florida scrub-jays have been known to decrease in fire-excluded areas [5]. See Quercus virginiana and other Quercus write-ups in the FEIS database. FIRE USE : Fire is essential for Florida scrub-jay habitat maintenance. Some authors have recommended burning Florida scrub oak stands at the very least every 20 to 30 years, depending on the growth rate of the oak [9]. Fire can be used to create and maintain stand openings essential for feeding [16]. In addition fires can rejuvenate decadent stands for nesting and food production. Cox [9] recommended following these parameters when using fire as a tool for Florida scrub-jay habitat maintenance: (1) leave scrub oaks less than 1.5 feet (1 m) high (2) burn oaks over 10.5 feet (3.5 m) high every 3 to 5 years maximum, and 15 to 20 years minimum (3) leave adequate habitat while the burned area recovers (4) burn in a mosaic to provide dense cover for nesting and create open space for feeding (5) if burning on a 10-year cycle, then burn 10 percent of the total area every year (6) if firebreaks are necessary, habitat should be divided into 25- to 50-acre (10-20 ha) parcels (7) if less than 5 percent of the area is bare ground, burn when oaks reach 6 to 9 feet (2-3 m) in height; if greater than 15 percent of the area is bare ground, burn when oaks reach 9 to 10.5 feet (3-3.5 m) in height

REFERENCES

WILDLIFE SPECIES: Aphelocoma coerulescens
REFERENCES : 1. American Ornithologists' Union. 2004. The A.O.U. check-list of North American birds, 7th edition, [Online]. American Ornithologists' Union (Producer). Available: http://www.aou.org/checklist/index.php3 [2005, January 10]. [50863] 2. Balda, Russell P. 1987. Avian impacts on pinyon-juniper woodlands. In: Everett, Richard L., compiler. Proceedings--pinyon-juniper conference; 1986 January 13-16; Reno, NV. Gen. Tech. Rep. INT-215. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 525-533. [4993] 3. Bent, Arthur Cleveland. 1964. Life histories of North American thrushes, kinglets, and their allies. New York: Dover Publications, Inc. 452 p. [24782] 4. 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] 5. Breininger, D. R.; Schmalzer, P. A. 1990. Effects of fire and disturbance on plants and birds in Florida oak/ palmetto scrub community. American Midland Naturalist. 123(1): 64-74. [9875] 6. Breininger, David R.; Smith, Rebecca B. 1992. Relationships between fire and bird density in coastal scrub and slash pine flatwoods in Florida. American Midland Naturalist. 127(2): 233-240. [17993] 7. Brown, David E. 1982. Great Basin montane scrubland. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 83-84. [8890] 8. Campbell, R. Wayne. 1986. First Canadian record of the scrub jay (Aphelocoma coerulescens). Canadian Field-Naturalist. 100: 120-121. [21969] 9. Cox, Jeffrey A. 1984. Distribution, habitat, and social organization of the Florida scrub jay, with a discussion of the coopertive breeding in New World jays. Gainesville, FL: University of Florida. 271 p. Dissertation. [17410] 10. DeGraaf, Richard M.; Scott, Virgil E.; Hamre, R. H.; [and others]. 1991. Forest and rangeland birds of the United States: Natural history and habitat use. Agric. Handb. 688. Washington, DC: U.S. Department of Agriculture, Forest Service. 625 p. [15856] 11. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 12. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; [and others]. 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] 13. Hall, Lisa; Balda, Russell P. 1988. The role of scrub jays in pinyon regeneration. Final report on Cooperative Agreement No. 28-06-397. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 36 p. [16755] 14. Kuchler, A. W. 1964. Manual to accompany the map of potential vegetation of the conterminous United States. Special Publication No. 36. New York: American Geographical Society. 77 p. [1384] 15. Mason, Robert B. 1981. Response of birds and rodents to controlled burning in pinyon-juniper woodlands. Reno, NV: University of Nevada. 55 p. Thesis. [1545] 16. Myers, Ronald L. 1990. Scrub and high pine. In: Myers, Ronald L.; Ewel, John J., eds. Ecosystems of Florida. Orlando, FL: University of Central Florida Press: 150-193. [17389] 17. Pase, Charles P. 1982. Californian (coastal) chaparral. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 91-94. [8891] 18. Terres, John K. 1980. The Audubon Society encyclopedia of North American birds. New York: Alfred A. Knopf. 1109 p. [16195] 19. U.S. Department of the Interior, Fish and Wildlife Service. 1994. Endangered and threatened wildlife and plants; animal candidate review for listing as endangered or threatened species; proposed rule. 50 CFR Part 17. Tuesday, November 15, 1994. Federal Register. 59(219): 58982-59028. [24357] 20. Vander Kloet, S. P.; Austin-Smith, P. J. 1986. Energetics, patterns and timing of seed dispersal in Vaccinium section Cyanococcus. American Midland Naturalist. 115: 386-396. [12523] 21. Westcott, Peter Walter. 1970. Ecology and behavior of the Florida scrub jay. Gainesville, FL: The University of Florida. 94 p. Dissertation. [17411] 22. Webber, H. J. 1935. The Florida scrub, a fire-fighting association. American Journal of Botany. 22: 344-361. [18493] 23. Woolfenden, Glen E. 1973. Nesting and survival in a population of Florida scrub jays. Living Bird. 12: 25-49. [16723] 24. Tate, James, Jr. 1986. The Blue List for 1986. American Birds. 40(2): 227-235. [24324] 25. Wood, Don A., compiler. 1994. Official lists of endangered & potentially endangered fauna and flora in Florida. Tallahassee, FL: Florida Game and Fresh Water Fish Commission. 22 p. [24196] 26. U.S. Department of the Interior, Fish and Wildlife Service. 1994. Endangered and threatened wildlife and plants. 50 CFR 17.11 & 17.12. Washington, DC: [Publisher unknown]. 42 p. [24413]


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