Index of Species Information
WILDLIFE SPECIES: Lynx rufus
Introductory
WILDLIFE SPECIES: Lynx rufus
AUTHORSHIP AND CITATION :
Tesky, Julie L. 1995. Lynx rufus. In: Fire Effects Information System, [Online].
U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station,
Fire Sciences Laboratory (Producer). Available:
www.fs.usda.gov/database/feis/animals/mammal/lyru/all.html [].
Revisions:
18 July 2013: DeGraaf, Richard M.; Rudis, Deborah D. 2001 citation corrected to
DeGraaf, Richard M.; Yamasaki, Mariko. 2001.
ABBREVIATION :
LYRU
COMMON NAMES :
bobcat
bay lynx
TAXONOMY :
The scientific name for bobcat is Lynx rufus (Schreber) [17,53,54,55].
Hall [17] recognizes 12 subspecies:
Lynx rufus baileyi Merriam
Lynx rufus californicus Mearns
Lynx rufus escuinapae J. A. Allen
Lynx rufus fasciatus Rafinesque
Lynx rufus floridanus Rafinesque
Lynx rufus gigas Bangs
Lynx rufus oaxacensis Goodwin
Lynx rufus pallescens Merriam
Lynx rufus peninsularis Thomas
Lynx rufus rufus
Lynx rufus superiorensis Peterson and Downing
Lynx rufus texensis Mearns
Bobcats hybridize with lynx (Lynx canadensis) [7].
SYNONYMS :
Felis rufus Schreber [52,56]
ORDER :
Carnivora
CLASS :
Mammal
FEDERAL LEGAL STATUS :
The Mexican bobcat (Lynx rufus escuinapae) is listed as Endangered [39].
OTHER STATUS :
Information on state- and province-level protection status of animals in the
United States and Canada is available at NatureServe, although recent changes
in status may not be included.
WILDLIFE DISTRIBUTION AND OCCURRENCE
WILDLIFE SPECIES: Lynx rufus
GENERAL DISTRIBUTION :
Bobcats occur from southern Canada south almost throughout the
contiguous United States to southern Mexico. They do not occur in most
of Iowa, Illinois, Indiana, Ohio, and Missouri. Bobcat range is
gradually expanding northward in Canada as boreal forests become
fragmented by farming, logging, and settlement [6,17]. The current
distribution of the subspecies was not described in the literature.
ECOSYSTEMS :
FRES10 White-red-jack pine
FRES11 Spruce-fir
FRES12 Longleaf-slash pine
FRES13 Loblolly-shortleaf pine
FRES14 Oak-pine
FRES15 Oak-hickory
FRES16 Oak-gum-cypress
FRES17 Elm-ash-cottonwood
FRES18 Maple-beech-birch
FRES19 Aspen-birch
FRES20 Douglas-fir
FRES21 Ponderosa pine
FRES22 Western white pine
FRES23 Fir-spruce
FRES24 Hemlock-Sitka spruce
FRES25 Larch
FRES26 Lodgepole 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
FRES36 Mountain grasslands
FRES37 Mountain meadows
FRES38 Plains grasslands
FRES39 Prairie
FRES40 Desert grasslands
FRES41 Wet grasslands
FRES42 Annual grasslands
FRES44 Alpine
STATES :
AL |
AK |
AZ |
AR |
CA |
CO |
CT |
DE |
FL |
GA |
ID |
IL |
IN |
IA |
KS |
KY |
LA |
ME |
MD |
MA |
MI |
MN |
MS |
MO |
MT |
NE |
NV |
NH |
NJ |
NM |
NY |
NC |
ND |
OH |
OK |
OR |
PA |
RI |
SC |
SD |
TN |
TX |
UT |
VT |
VA |
WA |
WV |
WI |
WY |
AB |
BC |
MB |
ON |
SK |
|
MEXICO |
BLM PHYSIOGRAPHIC REGIONS :
1 Northern Pacific Border
2 Cascade Mountains
3 Southern Pacific Border
4 Sierra Mountains
5 Columbia Plateau
6 Upper Basin and Range
7 Lower Basin and Range
8 Northern Rocky Mountains
9 Middle Rocky Mountains
10 Wyoming Basin
11 Southern Rocky Mountains
12 Colorado Plateau
13 Rocky Mountain Piedmont
14 Great Plains
15 Black Hills Uplift
16 Upper Missouri Basin and Broken Lands
KUCHLER PLANT ASSOCIATIONS :
Bobcats probably occur in most Kuchler plant associations.
SAF COVER TYPES :
Bobcats probably occur in most SAF cover types.
SRM (RANGELAND) COVER TYPES :
Bobcats probably occur in most SRM (rangeland) cover types.
PLANT COMMUNITIES :
Bobcats are found in a wide variety of plant communities including
coniferous forest, deciduous forest, mixed forest, the Everglades,
prairie and other grasslands, chaparral, sagebrush (Artemisia spp.)
scrubland, creosotebush (Larrea tridentata) scrubland, and mesquite
(Prosopis spp.) scrub [1].
Bobcats do show some plant community preferences. They commonly occur in
areas with a mosaic of different plant communities and seral stages
[4,7,51]. In Minnesota bobcats preferred areas of black spruce (Picea
mariana), northern white-cedar (Thuja occidentalis), and balsam fir
(Abies balsamea) interspersed with quaking aspen (Populus tremuloides)
and lowland shrubs [4]. No significant seasonal shifts in habitat use
occurred. Rollings [35] found that in Minnesota, bobcat winter habitat
was primarily thick northern white-cedar or black spruce swamps. In New
England, bobcats were frequently found in northern white-cedar swamps
and black spruce thickets [12]. Bobcat habitat in Massachusetts was
characterized by cliff areas, black spruce plantations, and eastern
hemlock (Tsuga canadensis)-hardwood communities [30].
Common tree and shrub species of bobcat habitat in the Intermountain
West include manzanita (Arctostaphylos spp.), mountain-mahogany
(Cercocarpus spp.), pinyon (Pinus spp.), sagebrush, and juniper
(Juniperus spp.) [37]. In the Frank-Church River of No Return
Wilderness, Idaho, bobcats selected Douglas-fir (Pseudotsuga
menziesii)/mountain-mahogany (Cercoparus spp.) communities, but avoided
Douglas-fir/wheatgrass communities. The latter communities lacked rocky
terrain and mountain-mahogany cover for bobcats [49]. Bobcats in
another Idaho study were found in areas dominated by big sagebrush
(Artemisia tridentata) with nearby caves and sagebrush-Utah juniper (J.
osteosperma) areas near volcanic outcroppings. Most of the preference
for these habitats was accounted for by prey density and cover for
hunting and resting [47]. In Fresno County, California, bobcats were
most common from 2,001 to 4,003 feet (610-1,220 m) elevation, with the
preferred cover types in the eastern portion of the county including
woodland-grass, pine (Pinus spp.)-chaparral, and hardwood woodland [7].
BIOLOGICAL DATA AND HABITAT REQUIREMENTS
WILDLIFE SPECIES: Lynx rufus
TIMING OF MAJOR LIFE HISTORY EVENTS :
Breeding season - Bobcats commonly breed in February and March.
However, variations in the breeding season are influenced by latitude,
longitude, altitude, climate, photoperiod, and perhaps prey
availability. Bobcats breed from February through July in Alabama,
peaking in March and April [7]. In Yellowstone National Park the peak
of the breeding season is from January through early March [9]. In the
Sierra Nevada bobcats breed from January through June, with breeding
peaking from February through May [41]. One male generally mates with
several females [9].
Age at first reproduction - Female bobcats are capable of breeding at 1
year of age. Males are sexually mature at 2 years of age [7,11]. Both
sexes remain reproductively active throughout life [11].
Gestation/litter size - Gestation is about 62 days [6,7]. In Utah a
majority of young are born in April or May [47], and in May and June in
Wyoming [11]. Usually two to three kittens are produced per litter,
although up to five kittens have been reported [9]. Generally, only one
litter is produced per year [41]. The kittens are raised solely by
their mother [9].
Development of young - Bobcats are born with their eyes closed. Their
eyes open between 3 and 11 days after birth. Bobcats are weaned at 7 to
8 weeks of age, but remain with their mother until they disperse [7].
Dispersal of juveniles - Juvenile bobcats generally disperse during
their first fall. In Michigan bobcat litters may not disperse until
their first spring [7].
Activities - Bobcats are generally crepuscular. Zezulak [46] found that
bobcat activity levels peaked at dawn and dusk in California. In
another California study, bobcat activity levels differed seasonally.
Bobcats were generally crepuscular during the winter, and more nocturnal
during the spring [48].
Life span - In the wild, most bobcats live 2 to 5 years; some
individuals live 15 years [9,11].
PREFERRED HABITAT :
Bobcats are adapted to a wide variety of habitats including swamps,
deserts, and mountain ranges [6,7]. Rollings [35] stated that prey
abundance, protection from severe weather, availability of rest areas
and cover, and freedom from human intrusion were the key factors in
bobcat habitat selection in Minnesota.
Typical bobcat habitat in the North is broken country including swamps,
bogs, conifer stands, and rocky ledges. Ledges appear to be the most
important terrain feature in bobcat habitat in the northern portion of
the range, with the only satisfactory replacement being conifers in bogs
and swamps. Courtship activities are often centered around ledges [7].
In Massachusetts bobcat courtship was invariably performed in the
vicinity of rocky ledges. Specific habitat requirements for courtship
have not been reported elsewhere [6].
In the South bobcats are common in mixed forest and agricultural areas
that have a high proportion of early to mid-successional stages [6,7].
In the hardwood bottomlands of Louisiana, Hall and Newsom [18] found
that mid-successional stages on cutover areas, characterized by
saplings, vines, and dense briar palmetto (Serenoa spp.), were the
centers of bobcat activity.
In the West bobcats prefer rocky canyons at elevations from 4,593 to
6,890 feet (1,400-2,100 m) with ledges and areas of dense vegetation.
In the southwestern and western United States, bobcats are adapted to
even the driest deserts if shade is available [37].
Home range - Bobcat home range estimates vary from 0.23 square mile (0.6
sq km) for California to 78 square miles (201 sq km) for Minnesota.
Females generally have smaller home ranges than males. The home ranges
of male and female bobcats may overlap, but home ranges of females
rarely overlap with each other. Seasonal range differences may also
occur. Winter ranges of male bobcats in California were up to 41
percent smaller than summer ranges. Female bobcats showed reductions in
their home range size up to 70 percent over the same period [7].
COVER REQUIREMENTS :
Denning and resting cover - Habitat features such as thickets, stumps,
logging debris, and various types of rock features serve as denning
sites and resting areas for bobcats [6]. Rock piles or broken rocky
ledges provide important den sites and shelter for bobcats, especially
in the West. Rocky areas were the preferred den sites of bobcats in
easteren Idaho [3]. In California small rocky areas were often used as
denning and resting sites [48]. During periods of heavy rain or high
temperatures, bobcats used these areas for shelter almost exclusively.
Bailey [2] noted the importance of rock piles and caves for rearing
young and for refuge in severe weather. In the northern part of the
bobcat's range, where winters are often severe, bobcats may require
underground dens to survive [3].
Bobcats also use brush piles, hollow trees, and logs as rest sites and
dens. Bobcat rest areas have frequently been found under low-hanging
conifer boughs [7]. Zezulak and Schwab [48] noted bobcats resting under
bushes and next to fallen Joshua trees (Yucca brevifolia) in the Mojave
Desert. In the relatively moderate climate of the Southeast, features
such as thickets, hollow stumps, and logging debris offer adequate cover
for both resting and denning [6].
Travel and loafing cover - Bottomland hardwoods are often used for
loafing and travel, possibly because the closed canopy and dense
midstory of these areas supply shade during periods of high temperatures
[6].
Foraging cover - Bobcats often hunt in open to semiopen areas. Bobcat
prey are generally less common in forested cover types than in
shrub/grass-forb cover types. Within the shrub/grass-forb cover types,
shrub patches or thickets are necessary cover for bobcat prey.
Favorable environments for bobcat prey (e.g., cotton rats [Sigmodon spp.]
and cottontail rabbits [Sylvilagus spp.]) in the Southeast are generally
available on clearcuts and young (< 5-year) pine plantations [6,57].
FOOD HABITS :
Bobcats are opportunistic and will attempt to take almost any prey
available, including insects, fish, amphibians, reptiles, birds, and
mammals. Mammalian prey, however, is often the most common prey in the
bobcat diet. Bobcats most frequently kill animals weighing 1.5 to 12
pounds (700 g-5.5 kg) [7].
Cottontail rabbits appear to be the principal prey of bobcats throughout
bobcat's range [6,7,38]. Primary exceptions occur from Minnesota to New
England, where white-tailed deer (Odocoileus virginianus) and snowshoe
hare (Lepus americanus) increase in importance [6].
Bobcats in the Southeast rely heavily on two species, eastern
cottontails (Sylvilagus floridanus) and cotton rats, for food throughout
the year [6]. Cotton rats may be more important than eastern
cottontails from Florida to Louisiana. In the interior highlands of
Arkansas, eastern fox squirrels (Sciurus niger) and eastern gray
squirrels (S. carolinensis) are important foods. In the mountains of
eastern Tennessee and western North Carolina, the woodland vole
(Microtus pinetorum) and various species of birds are important bobcat
prey [6]. In the West rodents, especially woodrats (Neotoma spp.), are
often eaten [6,7].
PREDATORS :
Bobcats are not commonly preyed upon. Kittens may be taken by foxes
(Vulpes spp. and Urocyon spp.), owls (Strigidae), mountain lions (Felis
concolor), coyotes (Canis latrans), and adult male bobcats. Bobcats may
also be killed or injured by prey animals. Bobcats are hunted and
trapped by humans [7].
MANAGEMENT CONSIDERATIONS :
To enhance and maintain habitat quality for bobcats, managers should
maintain a mosaic of cover types with early to mid-successional stages,
maintain cover adjacent to preferred physical features (e.g., cliffs),
and maintain vegetation in riparian areas and ridgelines to enhance
dispersal [1].
Habitat management favoring bobcats is possible in areas managed for
timber production. Generally, small mammal populations peak 1 to 3
years after clearcutting and planting and decrease sharply thereafter.
Clearcutting "small" blocks of timber interspersed with forested areas
provides good habitat for small mammals and therefore good foraging
habitat for bobcats. Delaying the canopy closure of newly planted
stands promotes small mammal abundance for longer periods. Canopy
closure can be delayed in several ways, including increased spacing (to
approximately 10 feet [3 m]) of original planting, and early and
extensive thinning [6].
Response to human activities - Bobcats appear capable of dealing with
moderate human influence on the environment. Their populations are
stable in the United States, except in areas of intensive farming and
dense human populations, such as in the Midwest and along the central
Atlantic coast in Delaware and New Jersey. In Canada, bobcats are
expanding their range into many areas that previously supported only
lynx [7].
Bobcats often use recently logged areas and farms, because logging and
farming practices often provide food and cover for prey species.
Agricultural land that is so extensive as to eliminate rocky ledges,
swamps, and forest tracts is not used by bobcats. Bobcats show little
or no aversion to human dwellings or equipment; in fact, one bobcat
frequently rested within 200 feet (61 m) of an occupied dwelling.
Resting bobcats often respond to motor vehicles and logging activities
by moving a short distance and resuming their rest [7].
Depredations - Bobcats occasionally prey upon livestock [7]. Gashwiler
and others [16] allege that bobcats often hunt around lambing grounds,
but domestic sheep remains were found in only 1 of 53 bobcat stomachs.
Only 1 of 222 ewe losses to predators in 1973 through 1975 in Idaho was
attributed to a bobcat [7].
FIRE EFFECTS AND USE
WILDLIFE SPECIES: Lynx rufus
DIRECT FIRE EFFECTS ON ANIMALS :
Bobcats are very mobile and can probably escape most fires. There are
no reports of direct bobcat mortality due to fire [32]. Howard and
others [22] saw a bobcat leaving burning brush in California, but found
no animals that had been injured or killed by the fire.
HABITAT RELATED FIRE EFFECTS :
Fire may improve the foraging habitat and prey base of bobcats. Fires
that create a mosaic of burned and unburned areas including some open
areas and some cover are probably most beneficial to bobcats. Fires
that reduce vegetation height and create open areas probably increase
hunting efficiency. Surface fires often open substrates for quieter
stalking and easier capture of prey than can occur in closed forests
[26]. Annual winter burning on a northern bobwhite (Colinus
virginianus) plantation may have improved stalking conditions for
bobcats which resulted in an increase in the local bobcat population
[31].
In California bobcats feed in recent (1-year-old) chaparral burns and
young (2- to 3-year-old) chaparral [28]. Longhurst [28] observed that
at the Hopland Field Station in California, populations of bobcats
increased in young to intermediate aged chaparral interspersed with
grassland. Bobcat populations showed a downward trend in both mature
chaparral (10 years old or more) and extensive grasslands.
Periodic fire helps to maintain habitat for many bobcat prey. Several
studies indicate that many small mammal populations increase rapidly
subsequent to fire in response to increased food availability
[20,21,26].
Cotton rats often leave burned areas immediately after fire, but they
return to burned areas to forage on green vegetation as the season
progresses. Cotton rats experience greater weight gains in burned than
unburned areas. Komarek [50] reported effects of fire exclusion on
cotton rats and other grassland rodents in pine woods which had
previously been burned annually. After 4 years the cotton rat
population had decreased sharply. Fire at 3-year intervals would
provide optimum habitat for cotton rats as long as adequate amounts of
unburned areas were available as escape cover. Cottontail rabbit
responses to fire are apparently similar to those of the cotton rat
[21]. Fire often improves hare and rabbit forage quality and quantity
for two or more growing seasons [20,26]. Hill [20] concluded that
burning in pine plantations in the Southeast at intervals longer than 2
years would be less beneficial to rabbits and hares than annual burns,
but any fire is better for these species than fire exclusion.
FIRE USE :
Prescribed burning that favors small mammals by creating ecotones and
different age classes of vegetation would increase the prey base for
bobcats and make hunting easier for them by opening up the habitat [33].
FIRE REGIMES :
Find fire regime information for the plant communities in which this
species may occur by entering the species name in the FEIS home page under
"Find Fire Regimes".
REFERENCES
WILDLIFE SPECIES: Lynx rufus
REFERENCES :
1. Allen, A. W. 1987. The relationship between habitat and furbearers. In:
Novak, Milan; Baker, J. A.; Obbard, M. E.; Malloch, Bruce, eds. Wild
furbearer management and conservation in North America. Ottawa, ON:
Ontario Ministry of Natural Resources: 164-179. [24997]
2. Bailey, Theodore N. 1974. Social organization in a bobcat population.
Journal of Wildlife Management. 38(3): 435-446. [25141]
3. Bailey, Theodore N. 1981. Den ecology, population parameters and diet of
eastern Idaho bobcats. In: Blum, L. G.; Escherich, P. C., eds. Bobcat
research conference: Proceedings; 1979 October 16-18; Front Royal, VA.
NWF Science and Technical Series No. 6. Washington, DC: National
Wildlife Federation: 62-69. [24985]
4. Berg, William E. 1981. Ecology of bobcats in northern Minnesota. In:
Blum, L. G.; Escherich, P. C., eds. Bobcat research conference:
Proceedings; 1979 October 16-18; Front Royal, VA. NWF Science and
Technical Series No. 6. Washington, DC: National Wildlife Federation:
55-61. [24983]
5. 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]
6. Boyle, Katherine A. 1987. Habitat suitability index models: bobcat.
Biol. Rep. 82 (10.147). Washington, DC: U.S. Department of the Interior,
Fish and Wildlife Service. 16 p. [11712]
7. Chapman, Joseph A.; Feldhamer, George A., eds. 1982. Wild mammals of
North America. Baltimore, MD: The Johns Hopkins University Press. 1147
p. [21085]
8. Clark, Mary K.; Lee, David S.; Funderburg, John B., Jr. 1985. The mammal
fauna of Carolina bays, pocosins, and associated communities in North
Carolina: an overview. Brimleyana. Raleigh, NC: North Carolina State
Museum of Natural History; 11: 1-38. [13478]
9. Clark, Tim W.; Harvey, Ann H.; Dorn, Robert D.; [and others], eds. 1989.
Rare, sensitive, and threatened species of the Greater Yellowstone
Ecosystem. Jackson, WY: Northern Rockies Conservation Cooperative,
Montana Natural Heritage Program, The Nature Conservancy, Mountain West
Environmental Services. 153 p. [16007]
10. Craig, Diana L. 1986. The seasonal food habits of sympatric populations.
of puma (Puma concolor), coyote (Canis latrans), and bobcat (Lynx rufus)
in the Diablo Range of California. San Jose, CA: San Jose State
University. 61 p. Thesis. [21364]
11. Crowe, Douglas M. 1975. Aspects of ageing, growth, and reproduction of
bobcats from Wyoming. Journal of Mammalogy. 56(1): 177-198. [25139]
12. DeGraaf, Richard M.; Yamasaki, Mariko. 1986. New England wildlife:
habitat, natural history, and distribution. Gen. Tech. Rep. NE-108.
Broomall, PA: U.S. Department of Agriculture, Forest Service,
Northeastern Forest Experiment Station. 491 p. [21386]
13. Dibello, Fred J.; Arthur, Stephen M.; Krohn, William B. 1990. Food
habits of sympatric coyotes, Canis latrans, red foxes, Vulpes vulpes,
and bobcats, Lynx rufus, in Maine. Canadian Field-Naturalist. 104:
403-408. [14121]
14. Eyre, F. H., ed. 1980. Forest cover types of the United States and
Canada. Washington, DC: Society of American Foresters. 148 p. [905]
15. 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]
16. Gashwiler, Jay S.; Robinette, W. Leslie; Morris, Owen W. 1960. Foods of
bobcats in Utah and eastern Nevada. Journal of Wildlife Management.
24(2): 226-229. [25136]
17. Hall, E. Raymond. 1981. The mammals of North America. 2nd ed. Vol. 2.
New York: John Wiley and Sons. 1271 p. [14765]
18. Hall, Harlan T.; Newsom, John D. 1976. Summer home ranges and movements
of bobcats in bottomland hardwoods of southern Louisiana. Proceedings,
Annual Conference of Southeastern Association of Fish and Wildlife
Agencies. 30: 427-436. [25127]
19. Herkert, J. R., ed. 1992. Endangered and threatened species of Illinois:
status and distribution. Volume 2--Animals. Springfield, IL: Illinois
Endangered Species Protection Board. 142 p. [23799]
20. Hill, Edward P. 1981. Prescribed fire and rabbits in southern forests.
In: Wood, Gene W., ed. Prescribed fire and wildlife in southern forests:
Proceedings of a symposium; 1981 April 6-8; Myrtle Beach, SC.
Georgetown, SC: Clemson University, Belle W. Baruch Forest Science
Institute: 103-108. [14816]
21. Hon, Tip. 1981. Effects of prescribed fire on furbearers in the South.
In: Wood, Gene W., ed. Prescribed fire and wildlife in southern forests:
Proceedings of a symposium; 1981 April 6-8; Myrtle Beach, SC.
Georgetown, SC: Clemson University, Belle W. Baruch Forest Science
Institute: 121-128. [14818]
22. Howard, W. E.; Fenner, R. L.; Childs, H. E., Jr. 1959. Wildlife survival
in brush burns. Journal of Range Management. 12: 230-234. [247]
23. Jones, James H.; Smith, Norman S. 1979. Bobcat density and prey
selection in central Arizona. Journal of Wildlife Management. 43(3):
666-672. [25135]
24. Jones, J. Knox, Jr.; Armstrong, David M.; Hoffman, Robert S.; Jones,
Clyde. 1983. Mammals of the Northern Great Plains. Lincoln, NE:
University of Nebraska Press. 375 p. [23862]
25. 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]
26. Landers, J. Larry. 1987. Prescribed burning for managing wildlife in
southeastern pine forests. In: Dickson, James G.; Maughan, O. Eugene,
eds. Managing southern forests for wildlife and fish: a proceedings;
[Date of conference unknown]; [Location of conference unknown]. Gen.
Tech. Rep. SO-65. New Orleans, LA: U.S. Department of Agriculture,
Forest Service, Southern Forest Experiment Station: 19-27. [11562]
27. Lawrence, George E. 1966. Ecology of vertebrate animals in relation to
chaparral fire in the Sierra Nevada foothills. Ecology. 47(2): 278-291.
[147]
28. Longhurst, William M. 1978. Responses of bird and mammal populations to
fire in chaparral. California Agriculture. 32(10): 9-12. [7639]
29. Marston, Merwin A. 1942. Winter relations of bobcats to white-tailed
deer in Maine. Journal of Wildlife Management. 6(4): 328-337. [25140]
30. McCord, Chet M. 1974. Selection of winter habitat by bobcats (Lynx rufus
on the Quabbin Reservation, Massachusetts. Journal of Mammalogy. 55(2):
428-437. [25138]
31. Miller, S. Douglas; Speake, Dan W. 1978. Prey utilization by bobcats on
quail plantations in southern Alabama. Proceedings, Annual Conference of
Southeastern Association of Fish and Wildlife Agencies. 32: 100-111.
[25137]
32. Nichols, R.; Menke, J. 1984. Effects of chaparral shrubland fire on
terrestrial wildlife. In: DeVries, Johannes J., ed. Shrublands in
California: literature review and research needed for management.
Contribution No. 191. Davis, CA: University of California, Water
Resources Center: 74-97. [5706]
33. Quinn, Ronald D. 1990. Habitat preferences and distribution of mammals
in California chaparral. Res. Pap. PSW-202. Berkeley, CA: U.S.
Department of Agriculture, Forest Service, Pacific Southwest Research
Station. 11 p. [15761]
34. Reynolds, Hudson G.; Johnson, R. Roy. 1964. Habitat relations of
vertebrates of the Sierra Ancha Experimental Forest. Res. Pap. RM-4.
Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky
Mountain Forest and Range Experiment Station. 16 p. [13485]
35. Rollings, Clair T. 1945. Habits, foods and parasites of the bobcat in
Minnesota. Journal of Wildlife Management. 9(2): 131-145. [24986]
36. Shiflet, Thomas N., ed. 1994. Rangeland cover types of the United
States. Denver, CO: Society for Range Management. 152 p. [23362]
37. Spowart, Richard A.; Samson, Fred B. 1986. Carnivores. In: Cooperrider,
Allan Y.; Boyd, Raymond J.; Stuart, Hanson R., eds. Inventory and
monitoring of wildlife habitat. Denver, CO: U.S. Department of the
Interior, Bureau of Land Management, Service Center: 475-496. [13526]
38. Trevor, John T.; Seabloom, Robert W.; Allen, Stephen H. 1989. Food
habits in relation to sex and age of bobcats from southwestern North
Dakota. Prairie Naturalist. 21(3): 163-168. [19877]
39. U.S. Department of the Interior, Fish and Wildlife Service. 2016.
Endangered Species Program, [Online]. Available: http://www.fws.gov/endangered/.
[86564]
40. Van Gelden, Richard George. 1982. Mammals of the National Parks.
Baltimore, MD: Johns Hopkins University Press. 310 p. [20893]
41. Verner, Jared; Boss, Allan S., tech. coords. 1980. California wildlife
and their habitats: western Sierra Nevada. Gen. Tech. Rep. PSW-37.
Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific
Southwest Forest and Range Experiment Station. 439 p. [10237]
42. Wagle, R. F. 1981. Fire: its effects on plant succession and wildlife in
the Southwest. Tucson, AZ: University of Arizona. 82 p. [4031]
43. Wirtz, William O., II. 1977. Vertebrate post-fire succession. In:
Mooney, Harold A.; Conrad, C. Eugene, technical coordinators. Symposium
on the environmental consequences of fire and fuel management in
Mediterranean ecosystems: Proceedings; 1977 August 1-5; Palo Alto, CA.
Gen. Tech. Rep. WO-3. Washington, DC: U.S. Department of Agriculture,
Forest Service: 46-57. [4801]
44. Wright, Henry A.; Bailey, Arthur W. 1982. Fire ecology: United States
and southern Canada. New York: John Wiley & Sons. 501 p. [2620]
45. Young, S. P. 1958. The bobcat of North America. Harrisburg, PA:
Stackpole Co.; Washington, DC: Wildlife Management Institute. 193 p.
[25142]
46. Zezulak, D. S. 1981. Northeastern California bobcat study. Aid in
Wildlife Restoration Project W-54-R-12; Job IV-3. Sacramento, CA:
California Department of Fish and Game. 19 p. [25143]
47. Zezulak, David S.; Schwab, Robert G. 1981. A comparison of density, home
range and habitat utilization of bobcat populations at Lava Beds and
Joshua Tree National Monuments, California. In: Blum, L. G.; Escherich,
P. C., eds. Bobcat research conference: Proceedings; 1979 October 16-18;
Front Royal, VA. NWF Science and Technical Series No. 6. Washington, DC:
National Wildlife Federation: 74-79. [24984]
48. Zezulak, D. S.; Schwab, R. G. 1980. Bobcat biology in a Mojave Desert
community. Federal Aid in Wildlife Restoration Project W-54-R-12, Job
IV-4. [Sacramento, CA]: California Department of Fish and Game. [Pages
unknown]. [24998]
49. Koehler, Gary M.; Hornocker, Maurice G. 1989. Influences of seasons on
bobcats in Idaho. Journal of Wildlife Management. 53(1): 197-202.
[13470]
50. Komarek, E. V. 1939. A progress report on southeastern mammal studies.
Journal of Mammalogy. 20: 292-299. [24987]
51. Rolley, Robert E. 1987. Bobcat. In: Novak, M.; Baker, J. A.; Obbard, M.
E.; Malloch, B., eds. Wild furbearer management and conservation in
North America. Ottawa: Ontario Ministry of Natural Resources: 670-681.
[25144]
52. Van Gelden, Richard G. 1977. Mammalian hybrids and generic limits.
American Museum Novitates. 2635: 1-25. [25332]
53. Leyhausen, P. 1979. Cat behavior. New York: Garland STPM Press. 340 p.
[25147]
54. Werdelin, Lars. 1981. The evolution of lynxes. Annales Zoologici
Fennici. 18: 37-71. [25333]
55. Honacki, J. H.; Kinman, K. E.; Koeppi, J. W., eds. 1982. Mammal species
of the world: a taxonomic and geographic reference. Lawrence, KS:
Association of Systematics Collections; Allen Press, Inc. [25146]
56. Corbet, G. B. 1978. The mammals of the pole arctic region: a taxonomic
review. London: British Museum of Natural History; Ithaca, NY: Cornell
University Press. 314 p. [25145]
57. Rolley, Robert E.; Warde, William D. 1985. Bobcat habitat use in
southeastern Oklahoma. Journal of Wildlife Management. 49(4): 913-920.
[25212]
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