|Black-tailed Jackrabbit range|
The black-tailed jackrabbit (Lepus californicus), also known as the American desert hare, is a common hare of the western United States and Mexico, where it is found at elevations from sea level to up to 10,000 feet (3,000 m). Reaching a length of about 2 feet (61 cm), and a weight from 3 to 6 pounds (1.4 to 2.7 kg), the black-tailed jackrabbit is the third largest North American hare, after the antelope jackrabbit and the white-tailed jackrabbit. The black-tailed jackrabbits occupy mixed shrub-grassland terrains. Their breeding depends on the location; it typically peaks in spring, but may continue all year round in warm climates. Young are born fully furred with eyes open; they are well camouflaged and are mobile within minutes of birth, thus females do not protect or even stay with the young except during nursing. The average litter size is around four, but may be as low as two and as high as seven in warm regions.
The black-tailed jackrabbit does not migrate or hibernate during winter and uses the same habitat of 0.4 to 1.2 square miles (1–3 km2) year-round. Its diet is composed of various shrubs, small trees, grasses and forbs. Shrubs generally comprise the bulk of fall and winter diets, while grasses and forbs are used in spring and early summer, but the pattern and plant species vary with climate. Black-tailed jackrabbit is an important prey species for raptors and carnivorous mammals, such as eagles, hawks, owls, coyotes, foxes, and wild cats. The rabbits host many ectoparasites including fleas, ticks, lice, and mites; for this reason, hunters often avoid collecting them.
Like other jackrabbits, the blacktail has distinctive long ears, and the long, powerful rear legs characteristic of hares. Reaching a length of about 2 feet (61 cm), and a weight from 3 to 6 pounds (1.4 to 2.7 kg), the black-tailed jackrabbit is the third largest North American hare, after the antelope jackrabbit and the white-tailed jackrabbit. The black-tailed jackrabbit's dorsal fur is agouti (dark buff peppered with black), and its undersides and the insides of its legs are creamy white. The ears are black-tipped on the outer surface, and unpigmented inside. The ventral surface of the tail is grey to white, and the black dorsal surface of the tail continues up the spine for a few inches to form a short, black stripe. The females are larger than males, with no other significant differences.
Taxonomy and distribution
Although seventeen subspecies are recognized, this number may be excessive. Using a cluster analysis of anatomical characters, Dixon and others found that black-tailed jackrabbit subspecies separated into two distinct groups that are geographically separated west and east of the Colorado Rocky Mountains and the Colorado River. They suggested only two infrataxa are warranted: the western subspecies L. c. californicus and the eastern subspecies L. c. texianus.
The black-tailed jackrabbit is the most widely distributed jackrabbit (Lepus spp.) in North America. Native black-tailed jackrabbit populations occur from central Washington east to Missouri and south to Baja California Sur and Zacatecas. Black-tailed jackrabbit distribution is currently expanding eastward in the Great Plains at the expense of white-tailed jackrabbit. The black-tailed jackrabbit has been successfully introduced in southern Florida and along the coastline in Maryland, New Jersey, and Virginia.
- Lepus californicus altamirae (Nelson)
- L. c. asellus (G. S. Miller)
- L. c. bennettii (Gray) – coastal southern California to Baja California Norte
- L. c. californicus (Gray) – coastal Oregon to coastal and Central Valley California
- L. c. curti (E. R. Hall)
- L. c. deserticola (Mearns) – southern Idaho to Sonora
- L. c. ememicus (J. A. Allen) – central Arizona to Sonora
- L. c. festinus (Nelson)
- L. c. magdalenae (Nelson)
- L. c. martirensis (J. M. Stowell)
- L. c. melanotis (Mearns) – South Dakota to Iowa, Missouri, and central Texas
- L. c. merriamai (Mearns) – south-central and southeastern Texas to Tamaulipas
- L. c. richardsonii (Bachman) – central California
- L. c. sheldoni (W. H. Burt)
- L. c. texianus (Waterhouse) – southeastern Utah and southwestern Colorado to Zacatecas
- L. c. wallawalla (Merriam) – eastern Washington to northeastern California and northwestern Nevada
- L. c. xanti (Thomas)
The black-tailed jackrabbit occupies plant communities with a mixture of shrubs, grasses, and forbs. Shrubland-herb mosaics are preferred over pure stands of shrubs or herbs. Black-tailed jackrabbit populations are common in sagebrush (Artemisia spp.), creosotebush (Larrea tridentata), and other desert shrublands; palouse, shortgrass, and mixed-grass prairies; desert grassland; open-canopy chaparral; oak (Quercus spp.) and pinyon-juniper (Pinus-Juniperus spp.) woodlands; and early seral (succeeding each other), low- to mid-elevation coniferous forests. It is also common in and near croplands, especially alfalfa (Medicago sativa) fields.
Major life events
Male black-tailed jackrabbits reach sexual maturity at about 7 months of age. Females usually breed in the spring of their second year, although females born in spring or early summer may breed in their first year. Ovulation is induced by copulation. The breeding season is variable depending upon latitude and environmental factors. In the northern part of its range in Idaho, black-tailed jackrabbit breeds from February through May. In Utah, black-tailed jackrabbit breed from January through July, with over 75% of females pregnant by April. The Kansas breeding season extends from January to August. Breeding in warm climates continues nearly year-round. Two peak breeding seasons corresponding to rainfall patterns and growth of young vegetation occur in California, Arizona, and New Mexico. In Arizona, for example, breeding peaks during winter (January–March) rains and again during June monsoons.
The gestation period ranges from 41 to 47 days. More litters are born in warm climates: the number of litters born each year ranges from two per year in Idaho to seven in Arizona. Litter sizes are largest in the northern portions of black-tailed jackrabbit's range and decrease toward the south. Average litter size has been reported at 4.9 in Idaho, 3.8 in Utah, and 2.2 in Arizona.
Female black-tailed jackrabbits do not prepare an elaborate nest. They give birth in shallow excavations called forms that are no more than a few centimeters deep. Females may line forms with hair prior to giving birth, but some drop litters in existing depressions on the ground with no further preparation. Young are borne fully furred with eyes open, and are mobile within minutes of birth. Females do not protect or even stay with the young except during nursing. Ages of weaning and dispersal are unclear since the young are well camouflaged and rarely observed in the field. Captive black-tailed jackrabbit are fully weaned by 8 weeks. The young stay together for at least a week after leaving the form.
The black-tailed jackrabbit can occupy a wide range of habitats as long as there is diversity in plant species. It requires mixed grasses, forbs, and shrubs for food, and shrubs or small trees for cover. It prefers moderately open areas without dense understory growth and is seldom found in closed-canopy habitats. For example, in California, black-tailed jackrabbit is plentiful in open chamise (Ademostoma fasciculatum Ceanothus spp.) chaparral interspersed with grasses, but does not occupy closed-canopy chaparral. Similarly, the black-tailed jackrabbit occupies clearcuts and early seral coniferous forest, but not closed-canopy coniferous forest.
Black-tailed jackrabbits do not migrate or hibernate during winter; the same habitat is used year-round. There is diurnal movement of 2 to 10 miles (3–16 km) from shrub cover in day to open foraging areas at night. Home range area varies with habitat and habitat quality. Home ranges of 0.4 to 1.2 square miles (1–3 km2) have been reported in big sagebrush (Artemisia tridentata) and black greasewood (Sarcobatus vermiculatus) communities of northern Utah.
Black-tailed jackrabbits require shrubs or small conifers for hiding, nesting, and thermal cover, and grassy areas for night feeding. A shrub-grassland mosaic or widely spaced shrubs interspersed with herbs provides hiding cover while providing feeding opportunities. Small shrubs do not provide adequate cover. In the Snake River Birds of Prey Study Area in southwestern Idaho, black-tailed jackrabbits were more frequent on sites dominated by big sagebrush or black greasewood than on sites dominated by the smaller shrubs winterfat (Krascheninnikovia lanata) or shadscale (Atriplex confertifolia). Black-tailed jackrabbits do not habitually use a burrow, although they has occasionally been observed using abandoned burrows for escape and thermal cover.
The black-tailed jackrabbit diet is composed of shrubs, small trees, grasses, and forbs. Throughout the course of a year, black-tailed jackrabbits feed on most if not all of the important plant species in a community. Growth stage and moisture content of plants may influence selection more than species. Shrubs generally comprise the bulk of fall and winter diets, while grasses and forbs are used in spring and early summer. This pattern varies with climate: herbaceous plants are grazed during greenup periods while the plants are in prereproductive to early reproductive stages, and shrubs are utilized more in dry seasons. Shrubs are browsed throughout the year, however. Most of a jackrabbit's (Lepus spp.) body water is replaced by foraging water-rich vegetation. Jackrabbits require a plant's water weight to be at least five times its dry weight in order to meet daily water intake requirements. Therefore, black-tailed jackrabbits switch to phreatophyte (deep-rooted) shrubs when herbaceous vegetation is recovering from their foraging.
Plant species used by black-tailed jackrabbits are well documented for desert regions. Forage use in other regions is less well known. However, black-tailed jackrabbits browse Douglas fir (Pseudotsuga menziesii), ponderosa pine (Pinus ponderosa), lodgepole pine (P. contorta), and western hemlock (Tsuga heterophylla) seedlings, and oak (Quercus spp.) seedlings and sprouts.
In Great Basin, big sagebrush is a primary forage species and is used throughout the year; in southern Idaho it forms 16–21% of the black-tailed jackrabbit summer diet. Rabbitbrush (Chrysothamnus spp.), spiny hopsage (Gray spinosa), and black greasewood are also browsed. Four-wing saltbush (Atriplex canescens) is heavily used in western Nevada. In Butte County, Idaho, winterfat comprises 41% of black-tailed jackrabbits' annual diet. Grasses comprise 14% of the diet, with most grass consumption in March and April. Russian thistle (Salsoda kali) is an important forb diet item. Needle-and-thread grass (Stipa comata) and Indian ricegrass (Oryzopsis hymenoides) are preferred grasses. Other preferred native grasses include Sandberg bluegrass (Poa secunda) and bluebunch wheatgrass (Pseudoroegneria spicata). Where available, crested wheatgrass (Agropyron desertorum and Agropyron cristatum) and barley (Hordeum vulgare) are highly preferred. Cheatgrass (Bromus tectorum) use is variable: it comprises 45% of the April diet on two southern Idaho sites, but black-tailed jackrabbit on an eastern Washington site do not use it.
In warm desert, mesquite (Prosopis spp.) and creosotebush (Larrea tridentata) are principal browse species. Broom snakeweed (Gutierrezia sarothrae) and Yucca spp. are also used. In honey mesquite (Prosopis glandulosa var. glandulosa) communities in New Mexico, the overall black-tailed jackrabbit diet was 47% shrubs, 22% grasses, and 31% forbs. Black grama (Bouteloua spp.), dropseed (Sporobolus spp.), fluffgrass (Erioneuron pulchellum), and threeawns (Aristida spp.) are the most commonly grazed grasses. Leather croton (Croton pottsii), silverleaf nightshade (Solanum elaeagnifolium), desert marigold (Baileya multiradiata), wooly paperflower (Psilostrophe tagetina), and globemallow (Sphaeralcea spp.) are important forbs, although many forb species are grazed. Opuntia spp., saguaro (Carnegiea gigantea), and other cacti are used throughout the year but are especially important in dry seasons as a source of moisture.
The black-tailed jackrabbit is an important prey species for many raptors and carnivorous mammals. The black-tailed jackrabbit and Townsend's ground squirrel (Spermophilus townsendii) are the two most important prey species on the Snake River Birds of Prey Study Area. Hawks preying on black-tailed jackrabbit include the ferruginous hawk (Buteo regalis), white-tailed hawk (Buteo albicaudatus), Swainson's hawk (B. swainsoni), and red-tailed hawk (B. jamaicensis). The black-tailed jackrabbit is the primary prey of Swainson's, red-tailed, and ferruginous hawks on Idaho and Utah sites. Other raptors consuming black-tailed jackrabbits include the great horned owl (Bubo virginianus), burrowing owl (Athene cunicularia), golden eagle (Aquila chrysaetos), and bald eagle (Haliaeetus leucocephalus). There is a significant correlation between golden eagle and black-tailed jackrabbit reproduction patterns. In Colorado and southeastern Wyoming, black-tailed jackrabbits constitute 9% of nesting bald eagles' diet. Jackrabbits (Lepus spp.) and cottontails (Sylvilagus spp.) combined form 9% of the diet of bald eagles wintering on National Forests in Arizona and New Mexico.
Mammalian predators include coyote (Canis latrans), bobcat (Lynx rufus), lynx (Lynx canadensis), domestic dog (Canis lupus familiaris), domestic cat (Felis catus), red fox (Vulpes vulpes), common gray fox (Urocyon cinereoargenteus), American badger (Taxidea taxus), wolf (Canis lupus), and mountain lion (Felis concolor). In many areas, black-tailed jackrabbit is the primary item in coyote diets. It is locally and regionally important to other mammalian predators. One study found that jackrabbits (Lepus spp.) made up 45% of the bobcat diet in Utah and Nevada. Another Utah–Nevada study found that jackrabbits were the fourth most commonly consumed prey of mountain lions.
Rattlesnakes (Crotalus spp.) and garter snakes (Thamnophis sirtalis) prey on black-tailed jackrabbit young. Raccoons (Procyon lotor) and striped skunks (Mephitis mephitis) may also capture young.
Parasites and disease
The black-tailed jackrabbit plays host to many ectoparasites including fleas, ticks, lice, and mites, and many endoparasites including trematodes, cestodes, nematodes, and botfly (Cuterebra) larvae. Diseases affecting the black-tailed jackrabbit in the West are tularemia, equine encephalitis, brucellosis, Q fever, and Rocky Mountain spotted fever. Ticks are vectors for tularemia, and infected ticks have been found on jackrabbits in the West. Jackrabbits infected with tularemia die very quickly.
The high prevalence of disease and parasites in wild jackrabbits affects human predation. Many hunters will not collect the jackrabbits they shoot, and those who do are well advised to wear gloves while handling carcasses and to cook the meat thoroughly to avoid contracting tularemia. Most hunting of jackrabbits is done for pest control or sport.
- Hoffman, R.S.; Smith, A.T. (2005). "Order Lagomorpha". In Wilson, D.E.; Reeder, D.M. Mammal Species of the World: A Taxonomic and Geographic Reference (3rd ed.). Johns Hopkins University Press. p. 196. ISBN 978-0-8018-8221-0. OCLC 62265494.
- Mexican Association for Conservation and Study of Lagomorphs (AMCELA), Romero Malpica, F.J. & Rangel Cordero, H. (2008). "Lepus californicus". IUCN Red List of Threatened Species. Version 2009.2. International Union for Conservation of Nature. Retrieved 1 February 2010.
- Whitaker, John O., Jr.; Hamilton, William J., Jr.. 1998. Mammals of the Eastern United States. Cornell University Press. 189-92. ISBN 0-8014-3475-0
- Big Bend National Park Black-tailed Jackrabbit, US National Park Service
- Flux, J. E. C. (1983). "Introduction to taxonomic problems in hares". Acta Zoologica Fennica 174: 7–10.
- Dixon, K. R. et al. (1983). "The New World jackrabbits and hares (genus Lepus).--2. Numerical taxonomic analysis". Acta Zoologica Fennica 174: 53–56.
- Chapman, J. A.; Dixon, K. R.; Lopez-Forment, W.; Wilson, D. E. (1983). "The New World jackrabbits and hares (genus Lepus).--1. Taxonomic history and population status". Acta Zoologica Fennica 174: 49–51.
- Dunn, John P.; Chapman, Joseph A.; Marsh, Rex E. (1982). "Jackrabbits: Lepus californicus and allies" in Chapman, J. A.; Feldhamer, G. A. (eds.) Wild mammals of North America: biology, management and economics. Baltimore, MD: The Johns Hopkins University Press. ISBN 0-8018-2353-6
- Hall, E. Raymond. (1951). "A synopsis of the North American Lagomorpha". University of Kansas Publications, Museum of Natural History 5 (10): 119–202.
- Nydegger, Nicholas C.; Smith, Graham W. (1986). "Prey populations in relation to Artemisia vegetation types in southwestern Idaho", pp. 152–156 in McArthur, E. Durant; Welch, Bruce L. (eds). Proceedings—symposium on the biology of Artemisia and Chrysothamnus; 1984 July 9–13; Provo, UT. Gen. Tech. Rep. INT-200. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station
- Mares, M. A.; Hulse, A. C. (1977). "Patterns of some vertebrate communities in creosote bush deserts", pp. 209–226 in: Mabry, T. J.; Hunziker, J. H.; DiFeo, D. R., Jr. (eds.) Creosote bush: Biology and chemistry of Larrea in New World deserts. U.S./IBP Synthesis Series 6. Stroudsburg, PA: Dowden, Hutchinson & Ross, Inc. ISBN 0879332824
- Hall, Lillian M.; George, Melvin R.; McCreary, Douglas D.; Adams, Theodore E. (1992). "Effects of cattle grazing on blue oak seedling damage and survival". Journal of Range Management 45 (5): 503–506. doi:10.2307/4002912. JSTOR 4002912.
- Giusti, Gregory A.; Schmidt, Robert H.; Timm, Robert M.; [and others]. 1992. The lagomorphs: rabbits, hares, and pika. In: Silvicultural approaches to animal damage management in Pacific Northwest forests. Gen. Tech. Rep. PNW-GTR-287. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station: 289–307
- Lechleitner, R. R. (1959). "Sex ratio, age classes and reproduction of the black-tailed jack rabbit". Journal of Mammalogy 40 (1): 63–81. doi:10.2307/1376117. JSTOR 1376117.
- Gross, Jack E.; Stoddart, L. Charles; Wagner, Frederic H. (1974). "Demographic analysis of a northern Utah jackrabbit population". Wildlife Monographs No. 40. Washington, DC: the Wildlife Society. JSTOR 4002912.
- Tiemeier, Otto W.; Plenert, Marvin L. (1964). "A comparison of three methods for determining the age of black-tailed jackrabbits". Journal of Mammalogy 45 (3): 409–416. doi:10.2307/1377413. JSTOR 1377413.
- Vorhies, Charles T.; Taylor, Walter P. (1933). "The life histories and ecology of jack rabbits, Lepus alleni and Lepus californicus ssp., in relation to grazing in Arizona". Technical Bulletin No. 49. Tucson, AZ: University of Arizona, Agricultural Experiment Station
- Smith, Graham W. (1990). "Home range and activity patterns of black-tailed jackrabbits". Great Basin Naturalist 50 (3): 249–256. JSTOR 41712598. PDF copy
- Johnson, Randal D.; Anderson, Jay E. (1984). "Diets of black-tailed jack rabbits in relation to population density and vegetation". Journal of Range Management 37 (1): 79–83. doi:10.2307/3898830. JSTOR 3898830.
- Bell, M. M.; Studinski, G. H. (1972). "Habitat manipulation and its relationship to avian and small rodent populations on the Decanso District of the Cleveland National Forest". Unpublished paper on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT
- Alipayou, Daniel (1993). "Range condition influences on Chihuahuan Desert cattle and jackrabbit diets". Journal of Range Management 46 (4): 296–301. doi:10.2307/4002461. JSTOR 4002461.
- Anderson, Jay E.; Shumar, Mark L. (1986). "Impacts of black-tailed jackrabbits at peak population densities on sagebrush vegetation". Journal of Range Management 39 (2): 152–155. doi:10.2307/3899289. JSTOR 3899289.
- Wansi, Tchouassi; Pieper, Rex D.; Beck, Reldon F.; Murray, Leigh W. (1992). "Botanical content of black-tailed jackrabbit diets on semidesert rangeland". Great Basin Naturalist 52 (4): 300–308.
- Woffinden, Neil D.; Murphy, Joseph R. (1989). "Decline of a ferruginous hawk population: a 20-year summary". Journal of Wildlife Management 53 (4): 1127–1132. doi:10.2307/3809619. JSTOR 3809619.
- Fagerstone, Kathleen A.; Lavoie, G. Keith; Griffith, Richard E., Jr. (1980). "Black-tailed jackrabbit diet and density on rangeland and near agricultural crops". Journal of Range Management 33 (3): 229–233. doi:10.2307/3898292. JSTOR 3898292.
- Brandt, C; Rickard, W (1994). "Alien taxa in the North American shrub-steppe four decades after cessation of livestock grazing and cultivation agriculture". Biological Conservation 68: 95. doi:10.1016/0006-3207(94)90339-5.
- Turner, Raymond M; Alcorn, Stanley M; Olin, George (1969). "Mortality of Transplanted Saguaro Seedlings". Ecology 50 (5): 835–844. doi:10.2307/1933697. JSTOR 1933697.
- Janes, Stewart W. (1985). "Habitat selection in raptorial birds", pp. 159–188 in Cody, Martin L. (ed.) Habitat selection in birds. Academic Press Inc. ISBN 0323140130
- Grubb, Teryl G.; Kennedy, Charles E. (1982). "Bald eagle winter habitat on southwestern National Forests". Res. Pap. RM-M237. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station
- Gashwiler, Jay S.; Robinette, W. Leslie; Morris, Owen W. (1960). "Foods of bobcats in Utah and eastern Nevada". Journal of Wildlife Management 24 (2): 226–228. doi:10.2307/3796754. JSTOR 3796754.
- Robinette, W. Leslie; Gashwiler, Jay S.; Morris, Owen W. (1959). "Food habits of the cougar in Utah and Nevada". Journal of Wildlife Management 23 (3): 261–273. doi:10.2307/3796884. JSTOR 3796884.
|Wikispecies has information related to: Lepus californicus|
|Wikimedia Commons has media related to Lepus californicus.|