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Introductory

WILDLIFE SPECIES: Aphelocoma coerulescens | Scrub Jay
ABBREVIATION : APCO COMMON NAMES : scrub jay TAXONOMY : The currently accepted scientific name for the scrub jay is Aphelocoma coerulescens (Bosc). Subspecies differences are based on size, coloration, and distribution. Subspecies of scrub jay are as follows [1,3]: Aphelocoma coerulescens ssp. coerulescens (Bosc)- Florida scrub jay A. coerulescens ssp. cana- Eagle Mountain srub jay A. coerulescens ssp. superciliosa (Strickland)- long-tailed scrub jay A. coerulescens ssp. oocleptica Swarth- Niasco scrub jay A. coerulescens ssp. californica (Vigors)- California scrub jay A. coerulescens ssp. woodhouseii (Baird)- Woodhouse's scrub jay A. coerulescens ssp. insularis Henshaw- Santa Cruz scrub jay A. coerulescens ssp. obscura Anthony- Belding's scrub jay A. coerulescens ssp. cactophila Huey- desert California scrub jay A. coerulescens ssp. hypoleuca Ridgway- Xantus' scrub jay A. coerulescens ssp. texana Ridgway- Texas scrub jay This report deals mainly with the Florida scrub jay, as information on the other subspecies is sparse. 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. Populations are noted on The Blue List as down to greatly down in Florida [24]. The Eagle Mountain scrub jay is federally listed as a Category 2 subspecies [19]. COMPILED BY AND DATE : S. A. Snyder, June 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Snyder, S. A. 1992. Aphelocoma coerullescens. In: Remainder of Citation

WILDLIFE DISTRIBUTION AND OCCURRENCE

WILDLIFE SPECIES: Aphelocoma coerulescens | Scrub Jay
GENERAL DISTRIBUTION : All but one subspecies of the scrub jay inhabit the West Coast and southwestern United States. 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]. One confirmed sighting of a scrub jay was noted in southern British Columbia [8]. Distributions by subspecies are listed below [1,3]: A. c. ssp. coerulescens - central Florida including the panhandle; occasionally Jekyll Island, Georgia A. c. ssp. superciliosa - southern Washington and Oregon; from San Francisco to the San Joaquin Valley, California A. c. ssp. oocleptica - from San Francisco to Humboldt, California A. c. ssp. californica - coastal southern California A. c. ssp. woodhouseii - southern Oregon, Idaho, Wyoming; western Colorado and Oklahoma, Arizona, Texas, Mexico; occasionally into Nebraska and Kansas A. c. ssp. insularis - Santa Cruz Island, California A. c. ssp. obscura - northwest Baja California A. c. ssp. cactophila - central Baja California A. c. ssp. hypoleuca - southern California from the coast to the high mountains A. c. ssp. texana - central Texas ECOSYSTEMS : FRES12 Longleaf-slash pine FRES14 Oak-pine FRES19 Aspen-birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES27 Redwood FRES28 Western hardwoods FRES29 Sagebrush FRES30 Desert shrub FRES31 Shinnery FRES32 Texas savanna FRES33 Southwestern shrubsteppe FRES34 Chaparral-mountain shrub FRES35 Pinyon-juniper FRES40 Desert grasslands STATES :
AR CA CO FL ID KS NE NV NM OK OR TX UT WA WY

MEXICO
BLM PHYSIOGRAPHIC REGIONS : 2 Cascade Mountains 3 Southern Pacific Border 4 Sierrra Mountains 5 Columbia Plateau 10 Wyoming Basin 11 Southern Rocky Mountains 12 Colorado Plateau 13 Rocky Mountain Piedmont 14 Great Plains KUCHLER PLANT ASSOCIATIONS : K006 Redwood forest K010 Ponderosa shrub forest K011 Western ponderosa forest K012 Douglas-fir forest K018 Pine - Douglas-fir forest K023 Juniper - pinyon woodland K024 Juniper steppe woodland K026 Oregon oakwoods K029 California mixed evergreen forest K030 California oakwoods K031 Oak - juniper woodland K033 Chaparral K034 Montane chaparral K037 Mountain-mahogany - oak scrub K038 Great Basin sagebrush K040 Saltbush - greasewood K043 Palo verde - cactus shrub K045 Ceniza shrub K046 Desert: vegetation largely lacking K056 Wheatgrass - needlegrass shrubsteppe K058 Grama - tobosa shrubsteppe K059 Trans-Pecos shrub savanna K079 Palmetto prairie K081 Oak savanna K084 Cross Timbers K086 Juniper - oak savanna K087 Mesquite - oak savanna K111 Oak - hickory - pine forest K112 Southern mixed forest K115 Sand pine scrub SAF COVER TYPES : 63 Cottonwood 69 Sand pine 71 Longleaf pine - scrub oak 72 Southern scrub oak 84 Slash pine 85 Slash pine - hardwood 89 Live oak 111 South Florida slash pine 210 Interior Douglas-fir 217 Aspen 222 Black cottonwood - willow 229 Pacific Douglas-fir 232 Redwood 233 Oregon white oak 234 Douglas-fir - tanoak - Pacific madrone 235 Cottonwood - willow 237 Interior ponderosa pine 239 Pinyon - juniper 241 Western live oak 243 Sierra Nevada mixed conifer 244 Pacific ponderosa pine - Douglas-fir 248 Knobcone pine 249 Canyon live oak 250 Blue oak - Digger pine 255 California coast live oak SRM (RANGELAND) COVER TYPES : NO-ENTRY PLANT COMMUNITIES : In Florida the 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]. In coastal California, the scrub jay inhabits chaparral communities of chamise (Adenostoma fasciculatum), hoary leaf ceanothus (Ceanothus crassifolius), and California scrub oak (Q. dumosa) [17]. The scrub jay also inhabits the redwood (Sequoia sempervirens), scrub oak, and pinyon (Pinus edulis)/juniper (Juniperus spp.) forests of the West. In the Great Basin the scrub jay inhabits montane scrub communities of Gambel oak (Q. gambelii) and mountain-mahogany (Cercocarpus spp.) [7]. REFERENCES : NO-ENTRY

BIOLOGICAL DATA AND HABITAT REQUIREMENTS

WILDLIFE SPECIES: Aphelocoma coerulescens | Scrub Jay
TIMING OF MAJOR LIFE HISTORY EVENTS : Courtship - As early as January (for Florida subspecies); 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]. In the West scrub jays build their nests in pinyon pine (Pinus spp.) and other scrubby vegetation [10]. They also frequent willow-lined (Salix spp.) streambanks and scrubby mountain foothills [18]. During winter they sometimes are found near cultivated fields. Scrub jays have been reported at elevations of 6,000 to 9,000 feet (1,829-2,743 m) in Colorado [18]. In other areas of the Great Basin, scrub jays are found from 7,550 to 9,000 feet (2,300-2,750 m) in elevation [7]. 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 bareground or vegetation less than 5.9 inches (15 cm) high covering 10 to 30 percent of the home range [9]. FOOD HABITS : 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]. Acorns and pinyon pine seeds are two of the most important plant foods. 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 : Because it caches nuts, the scrub jay can have a significant impact on the regeneration of pinyon pine and its distribution and density [2,13]. In Florida the 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 scrub jays can recolonize clearcut stands more quickly than burned stands [9]. REFERENCES : NO-ENTRY

FIRE EFFECTS AND USE

WILDLIFE SPECIES: Aphelocoma coerulescens | Scrub Jay
DIRECT FIRE EFFECTS ON ANIMALS : Fires during the nesting season may destroy scrub jay nests. HABITAT RELATED FIRE EFFECTS : Fire-destroyed habitat can force 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]. A prescribed burn in Nevada did not enhance scrub jay populations; scrub jay was the only "ground-dependent" bird not to increase following the burn [15]. 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. Scrub jay populations did not show a significant increase following a late November prescribed fire in oak/palmetto palm scrub in central Florida [5]. 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 FEIS database. FIRE USE : Fire is essential for 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 : NO-ENTRY

REFERENCES

WILDLIFE SPECIES: Aphelocoma coerulescens | Scrub Jay
REFERENCES : 1. Donohoe, Robert W. 1974. American hornbeam Carpinus caroliniana Walt. In: Gill, John D.; Healy, William M., eds. Shrubs and vines for northeastern wildlife. Gen. Tech. Rep. NE-9. Upper Darby, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station: 86-88. [13714] 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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