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Wildlife, Animals, and Plants
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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 |
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]
Index
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