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Overview

Brief Summary

Description

Black-tailed Jackrabbits are tremendous leapers, able to jump more than 6 m horizontally. They live in some of the hottest and driest regions of the continent, can survive on poor-quality foods, and get most or all of the water they need from their food. Where they can, they eat green vegetation, but they can survive in parts of the Southwest where creosote-bush forms a large part of their diet. They cope with extreme heat by lowering their metabolism and resting in the shade during the day, which conserves water. They get rid of extra salt through their urine, and blood flows close to the skin in their enormous ears, a cooling mechanism. Although mostly nocturnal and solitary, large groups sometimes form near a good food supply. With their typically high reproductive output, Black-tails can be agricultural pests, and there were periods in the 1800s and 1900s when aggressive rabbit drives herded and destroyed 5,000-6,000 animal in a single day. In spite of this, they are quite common and widespread.

Links:
Mammal Species of the World
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  • Original description: Gray, J.E., 1837.  Description of some new or little known Mammalia, principally in the British Museum Collection, p. 586.  The Magazine of Natural History, and Journal of Zoology, Botany, Mineralogy, Geology, and Meteorology, New Series, 1:577-587.
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Distribution

Range Description

Lepus californicus is widely distributed across Mexico and the USA (Flinders and Chapman 2003). Its range in Mexico includes the states of Hidalgo, Queretaro, northern Guanajuato, San Luis Potosi, eastern Tamaulipas, Zacatecas, Aguascalientes, eastern Durango, Chihuahua (excluding the southwest region), the extreme northeast region of Jalisco, Coahuila, Nuevo Leon, northern Sonora, and the entire Baja peninsula (Flinders and Chapman 2003). In the USA its range includes Texas, New Mexico, Arizona, Nevada, eastern Colorado, Nebraska, Kansas, most of Oklahoma including an isolated population in eastern section of the state, western Missouri, Utah (excluding the northeast), California (excluding part of the central region), most of Oregon (excluding western and central regions), southeast Washington, southern Idaho, and isolated population in Montana, and the extreme western region and southeast portion of Wyoming (Flinders and Chapman 2003). L. californicus was successfully introduced into Massachusetts, Maryland, New Jersey, Virginia and southern Florida (Flinders and Chapman 2003). It occurs in elevations ranging from - 84 m to 3,750 m (Flinders and Chapman 2003).
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Geographic Range

Lepus californicus is found throughout the southwestern United States into Mexico, as far east as Missouri, north into Washington, Idaho, Colorado and Nebraska, and west to California and Baja California.

Biogeographic Regions: nearctic (Native )

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occurs (regularly, as a native taxon) in multiple nations

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National Distribution

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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Global Range: Western North America, from the Pacific Coast east to Missouri and Arkansas, and from Washington, Idaho, southwestern Montana, eastern Wymong, and South Dakota south to Baja California, northern Sonora, southern Queretaro, and Hidalgo, central Mexico (Jones et al. 1983; Hoffmann, in Wilson and Reeder 1993; Best 1996). Releases have been made in Florida, New Jersey, Maryland, Massachusetts, and Virginia (see Best 1996).

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Physical Description

Morphology

Physical Description

Black-tailed jackrabbits measure 47-63 cm from nose to rump, the tail is between 50-112 mm and the ears are 10-13 cm long. As they are true hares, black-tailed jackrabbits are lankier and leaner than rabbits, have longer ears and legs, and the leverets are born fully-furred and open-eyed. Black-tailed jackrabbits possess a characteristic black stripe down the center of the back, a black rump patch, and the tail is black dorsally. Both sexes look alike, but the female is the larger of the two sexes.

Range mass: 1.3 to 3.1 kg.

Range length: 47 to 63 cm.

Other Physical Features: endothermic ; homoiothermic; bilateral symmetry

Sexual Dimorphism: female larger

Average basal metabolic rate: 7.314 W.

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Size

Length: 63 cm

Weight: 3600 grams

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Size in North America

Length:
Range: 465-630 mm

Weight:
Range: 1,300-3,300 g
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
L. californicus is capable of inhabiting many types of habitat (Flinders and Chapman 2003). This species is positively associated, in terms of abundance and distribution, with overgrazing by domestic livestock (Flinders and Chapman 2003). Diet is also variable for this species, dependent upon vegetation availability and location (Flinders and Chapman 2003). Generally, grasses and forbs are selected during the summer, while shrubs are chosen during winter months (Flinders and Chapman 2003). Variability in home range size is due to multiple factors like cover, predators, and competition (Flinders and Chapman 2003). L. californicus exhibits crepuscular feeding behavior (Flinders and Chapman 2003).

The total length of L. californicus is 46.5-63.0 cm (Hall and Kelson 1959). The breeding season is variable, contingent on latitude and environmental factors (Flinders and Chapman 2003). In Idaho the season is restricted to February to May (French et al. 1965). Where distribution occurs at lower latitudes the breeding season extends; in the southwestern USA it may last from early January to September (Griffing and Davis 1976). Gestation is variable but ranges from 40-47 days (Flinders and Chapman 2003). The litter size varies from 3.8-4.4 in the north to three to six in the south, giving a total output per female per year of about 10-14 (Best 1996). Total length at birth is variable dependent upon litter size, but a measurement in Arizona gave a length of 14.0 cm (Vorhies and Taylor 1933). Adult mortality is approximately 57%, while juvenile mean mortality ranges from 59-63% (Flinders and Chapman 2003).

Systems
  • Terrestrial
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Habitat

Black-tailed jackrabbits inhabit desert scrubland, prairies, farmlands, and dunes. They favor arid regions and areas of short grass rangeland from sea level to about 3,800 m. Many different vegetation types are used, including sagebrush-creosote bush, mesquite-snakeweed and juniper-big sagebrush. They also frequent agricultural areas where they can impact fruit and grain crops.

Range elevation: 3800 (high) m.

Habitat Regions: temperate ; terrestrial

Terrestrial Biomes: desert or dune ; savanna or grassland ; chaparral

Other Habitat Features: suburban ; agricultural

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Comments: Inhabits open plains, fields and deserts; open country with scattered thickets or patches of shrubs (Caire et al. 1989). Rests by day in shallow depression (form).

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Migration

Non-Migrant: Yes. At least some populations of this species do not make significant seasonal migrations. Juvenile dispersal is not considered a migration.

Locally Migrant: No. No populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).

Locally Migrant: No. No populations of this species make annual migrations of over 200 km.

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Trophic Strategy

Food Habits

Grasses and herbaceous matter are the preferred foods of Lepus californicus, but twigs and young bark of woody plants are the staple food when other plants are not available. Sagebrush and cacti are also taken. Jackrabbits eat almost constantly and consume large quantities relative to their size; 15 jackrabbits eat as much as a large grazing cattle in one day. Black-tailed jackrabbits do not require much water and obtain nearly all the water they need from the plant material they consume.

Plant Foods: leaves; roots and tubers; wood, bark, or stems; fruit

Primary Diet: herbivore (Folivore )

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Comments: Forages on grasses, forbs, crops and hay in summer; buds, bark, leaves of woody plants in winter. Obtains water from vegetation. Reingests soft fecal pellets produced while resting.

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Associations

Known predators

Lepus californicus (rabbit carcass (L. californicus)) is prey of:
Aquila chrysaetos
Buteo regalis
Buteo swainsoni
Blaesoxipha plinthopyga
Cochyliomyia macellaria
Musca domestica
Boreocanthon puncticollis
Dermestes marmoratus
Eleodes carbonarius
Eleodes longicollis
Embaphion
Silpha truncata
Necrophorus marginatus
Conomyrma bicolor
Pheidole
Novomessor cockerelli
Crematogaster clara
Iridomyrmex pruinosum
Trox suberosus

Based on studies in:
USA: California, Cabrillo Point (Grassland)
USA: Texas, Franklin Mtns (Carrion substrate)

This list may not be complete but is based on published studies.
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Known prey organisms

Lepus californicus (rabbit carcass (L. californicus)) preys on:
Bouteloua gracilis
Kochia
Sphaeralcea coccinea
Decapoda
Carex
Sporobolus cryptandrus
Pascopyrum smithii
Vulpia octoflora
Agropyron desertorum
Medicago sativa
Salsola
Mirabilis
Sophora nuttalliana

Triticum aestivum
Avena sativa
Helianthus annuus

Based on studies in:
USA: California, Cabrillo Point (Grassland)

This list may not be complete but is based on published studies.
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General Ecology

Populations are known to fluctuate markedly, slowly reaching peak over several years, falling off rapidly in several weeks or months (Larrison and Johnson 1981). Populations increase with overgrazing. Commonly carries tularemia. May travel up to a mile from daytime retreat to night feeding area. May gather in large group to feed. Home range varies from less than 1 sq km to 3 sq km in northern Utah (Smith 1990).

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Life History and Behavior

Cyclicity

Comments: Active throughout the year. Primarily crepuscular and nocturnal.

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Life Expectancy

Lifespan/Longevity

Average lifespan

Status: captivity:
6.8 years.

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Lifespan, longevity, and ageing

Maximum longevity: 11.8 years (captivity) Observations: One wild born specimen was about 11.8 years of age when it died in captivity (Richard Weigl 2005).
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Reproduction

Reproduction

Black-tailed jackrabbit males and females leap after, chase, and behave aggressively towards each other during a brief courtship phase before mating.

Mating System: polygynandrous (promiscuous)

Breeding season for Lepus californicus extends from December through September in Arizona and from late January to August in California and Kansas. Females produce 3 or 4 litters annually with 1-6 leverets (generally 3 or 4) after a 41-47 day gestation period. The young are precocial; females only nurse their offspring for 2-3 days and are not seen with their young after that time. Lifespan in captivity is 5-6 years, but rabbits in the wild often die much sooner due to predation, disease or problems associated with overpopulation.

Range number of offspring: 1 to 8.

Average number of offspring: 2.26.

Range gestation period: 41 to 47 days.

Average gestation period: 43 days.

Range weaning age: 14 to 21 days.

Average birth mass: 84.34 g.

Average number of offspring: 1.

Average age at sexual or reproductive maturity (female)

Sex: female:
243 days.

Parental Investment: precocial

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Breeding period may extend from late winter to late summer. Gestation lasts 41-47 days. Females produce 1-4 litters of 1-8 (usually 2-4) precocial young each year (Jones et al. 1983).

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Evolution and Systematics

Functional Adaptations

Functional adaptation

Large ears used to cool off: jackrabbit
 

The large ears of the jack rabbit are used in cooling, radiating heat via an extensive network of blood vessels.

     
  "Many desert animals have large ears, and the jack rabbit is no exception. It has been suggested that large ears, with their network of blood vessels, may serve to radiate heat to the sky while the animal is resting in the shade, so helping to lower its body temperature." (Foy and Oxford Scientific Films 1982:165)

"Blood flow to the ear pinnae is curtailed at ambient temperatures of between 1.4° and 24.0° C, which minimizes heat loss across the pinnae and allows the surfaces of erect pinnae to approach ambient temperature. The pinnae are warmed by steady or pulsatile vasodilation in some animals when the ambient temperature is between 1° and 9° C below body temperature, a response favoring heat loss. When ambient temperature exceeds body temperature by 4° to 5° C, the pinnae are circulated with blood cooler than ambient temperature; this response favors heat influx." (Hill and Vegth 1976:436)
  Learn more about this functional adaptation.
  • Foy, Sally; Oxford Scientific Films. 1982. The Grand Design: Form and Colour in Animals. Lingfield, Surrey, U.K.: BLA Publishing Limited for J.M.Dent & Sons Ltd, Aldine House, London. 238 p.
  • Mohler FS; Heath JE. 1988. Comparison of IR thermography and thermocouple measurement of heat loss from rabbit pinna. American Journal of Physiology - Regulatory Integrative and Comparative Physiology. 254(2): 389-395.
  • Wathen P; Mitchell JW; Porter WP. 1971. Theoretical and experimental studies of energy exchange from jackrabbit ears and cylindrically shaped appendages. Biophysical Journal. 11(12): 1030-1047.
  • Hill RW; Vegthe JH. 1976. Jackrabbit ears: surface temperatures and vascular responses. Science. 194(4263):
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Molecular Biology and Genetics

Molecular Biology

Statistics of barcoding coverage: Lepus californicus

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 0
Species: 115
Species With Barcodes: 1

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2008

Assessor/s
Mexican Association for Conservation and Study of Lagomorphs (AMCELA), Romero Malpica, F.J. & Rangel Cordero, H.

Reviewer/s
Smith, A.T. & Johnston, C.H. (Lagomorph Red List Authority)

Justification
Lepus californicus is a widespread species, whose range is expanding.

History
  • 1996
    Lower Risk/least concern
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Conservation Status

Population numbers of black-tailed jackrabbits are sometimes quite high despite attempts at culling their populations by ranchers and farmers. Population densities often reach 470 animals per square km, with densities as high as 1500 animals per square km being recorded. Large herding attempts have netted as much as 6,000 hares at a time. As with many hares, Lepus californicus populations undergo drastic fluctuations, with population numbers peaking every 6 to 10 years. In some years more then 90 per cent of western populations die from tularemia, which may or may not be related to the population cycling phenomenon. Because of their incredible fecundity, black-tailed jackrabbit numbers quickly recover from these kinds of die-offs.

Black-tailed jackrabbit populations are not threatened in general, though extensive habitat destruction may reduce suitable habitat.

US Federal List: no special status

CITES: no special status

IUCN Red List of Threatened Species: least concern

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National NatureServe Conservation Status

United States

Rounded National Status Rank: N5 - Secure

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NatureServe Conservation Status

Rounded Global Status Rank: G5 - Secure

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Population

Population
In the Reserva de la Biosfera de Mapimi:
14-37 individuals/km² shrublands
12-44 individuals/km² grassland.

Population Trend
Stable
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Threats

Threats

Major Threats
L. californicus is at risk from hunting for sport and local subsistence, human perturbation and exotic predation. In some places the animal competition (livestock), habitat fragmentation and human-induced fire represent important threats for their populations.
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Management

Conservation Actions

Conservation Actions
The following conservation measures are recommended for L. californicus, research in monitoring/trends and species-based action regarding harvest management. Long-term research is recommended with regard to ecological relationships and population dynamics and genetics (Flinders and Chapman 2003). There is also a need for more definitive classification of jackrabbit subspecies (Flinders and Chapman 2003). Furthermore, data are needed to determine gaps in distribution and relationship dynamics between L. californicus and other jackrabbits that occur sympatrically (Flinders and Chapman 2003).
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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Negative

Due to the removal of natural predators, such as coyote and kit fox, by European settlers, black-tailed jackrabbit populations have undergone incredible population explosions in which crops, orchards, and rangelands have suffered. They do considerable damange to farms, forest plantations, and young trees.

Negative Impacts: crop pest

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Economic Importance for Humans: Positive

As with many other Lepus species, L. californicus has been widely used as food for humans, especially by Native Americans. Their fur is not durable nor valuable, but it has been extensively used in the manufacture of felt and as trimming and lining for garments and gloves.

Positive Impacts: food ; body parts are source of valuable material

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Economic Uses

Comments: Sometimes regarded as a pest in certain areas; may damage rangeland, hayfields, and cultivated crops in years of abundance.

Hunted for sport and food. When very abundant, may be herded and killed; meat has been used for dog food (Caire et al. 1989).

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Wikipedia

Black-tailed jackrabbit

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 borne 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.

Contents

Description

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.[3] The females are larger than males, with no other significant differences.[4]

Taxonomy and distribution

Although seventeen subspecies are recognized, this number may be excessive.[5] Using 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.[6]

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.[5] Black-tailed jackrabbit has been successfully introduced in southern Florida and along the coastline in Maryland, New Jersey, and Virginia.[7][8]

Distribution of subspecies occurring entirely or partially in the United States is as follows [8][9]:

  • 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)

Plant communities

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 is common in sagebrush (Artemisia spp.),[10] creosotebush (Larrea tridentata),[11] and other desert shrublands; palouse, shortgrass, and mixed-grass prairies; desert grassland; open-canopy chaparral; oak (Quercus spp.)[12] and pinyon-juniper (Pinus-Juniperus spp.)[8] woodlands; and early seral (succeeding each other), low- to mid-elevation coniferous forests.[13] It is also common in and near croplands, especially alfalfa (Medicago sativa) fields.[8]

Major life events

Male black-tailed jackrabbit reach sexual maturity at about 7 months of age.[14] 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.[8] 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,[15] with over 75% of females pregnant by April. The Kansas breeding season extends from January to August.[16] Breeding in warm climates continues nearly year-round. Two peak breeding seasons corresponding to rainfall patterns and growth of young vegetation occur in California,[14] Arizona,[17] and New Mexico. In Arizona, for example, breeding peaks during winter (January–March) rains and again during June monsoons.[17]

The gestation period ranges from 41 to 47 days.[15] 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.[17] 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,[15] and 2.2 in Arizona.[17]

Female black-tailed jackrabbit 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.[16] Young are borne fully furred with eyes open, and are mobile within minutes of birth.[8] Females do not protect or even stay with the young except during nursing.[18] 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.[17] The young stay together for at least a week after leaving the form.[8][18]

Preferred habitat

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.[19] 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.[20] Similarly, black-tailed jackrabbit occupies clearcuts and early seral coniferous forest, but not closed-canopy coniferous forest.[13]

Black-tailed jackrabbit does not migrate or hibernate during winter;[8][13] 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.[8] Home range area varies with habitat and habitat quality.[13] 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.[18]

Black-tailed Jackrabbit camouflage.

Black-tailed jackrabbit require shrubs or small conifers for hiding, nesting, and thermal cover, and grassy areas for night feeding.[8][19] 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.[19][21] In the Snake River Birds of Prey Study Area in southwestern Idaho, black-tailed jackrabbit was 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 jackrabbit does not habitually use a burrow,[10] although it has occasionally been observed using abandoned burrows for escape and thermal cover.[8][17][18]

Food habits

The black-tailed jackrabbit diet is composed of shrubs, small trees, grasses, and forbs. Throughout the course of a year, black-tailed jackrabbit feed on most if not all of the important plant species in a community.[22] 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.[22][23] Shrubs are browsed throughout the year, however. Most of a jackrabbit's (Lepus spp.) body water is replaced by foraging water-rich vegetation.[17][24] Jackrabbit 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.[24]

Plant species used by black-tailed jackrabbit are well documented for desert regions. Forage use in other regions is less well known. However, black-tailed jackrabbit 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.[12][13]

Great Basin

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.[22][25] 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 (Salsola 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,[25] but black-tailed jackrabbit on an eastern Washington site do not use it.[26]

Warm desert

In warm desert, mesquite (Prosopis spp.) and creosotebush (Larrea tridentata) are principle browse species.[11][17] Broom snakeweed (Gutierrezia sarothrae) and Yucca spp. are also used. In honey mesquite (Prosopis glandulosa var. glandulosa) communities in New Mexico, overall black-tailed jackrabbit diet was 47% shrubs, 22% grasses, and 31% forbs.[21] Black grama (Bouteloua spp.), dropseed (Sporobolus spp.), fluffgrass (Erioneuron pulchellum), and threeawns (Aristida spp.) are the most commonly grazed grasses.[21][23] 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.[23] 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.[27]

Predators

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.[10] 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).[28] The black-tailed jackrabbit is the primary prey of Swainson's, red-tailed, and ferruginous hawks on Idaho and Utah sites.[28] Other raptors consuming black-tailed jackrabbit 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 production and black-tailed jackrabbit productivity.[10] In Colorado and southeastern Wyoming, black-tailed jackrabbit 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.[29]

Mammalian predators include coyote (Canis latrans), domestic dog (C. familiaris), red fox (Vulpes vulpes), common gray fox (Urocyon cinereoargenteus), American badger (Taxidea taxus), mountain lion (Felis concolor), housecat (F. catus), and bobcat (Lynx rufus).[8][13][16] 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.[30] Another Utah–Nevada study found that jackrabbits were the fourth most commonly consumed prey of mountain lion.[31]

Rattlesnakes (Crotalus spp.) and garter snakes (Thamnophis sirtalis) prey on black-tailed jackrabbit young.[14][17] Raccoons (Procyon lotor) and striped skunks (Mephitis mephitis) may also capture young.[17]

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 (Cutereba) 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 tuleremia die very quickly.[3]

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.[8]

References

 This article incorporates public domain material from the United States Department of Agriculture document "Lepus californicus".

  1. ^ Hoffman, Robert S.; Smith, Andrew T. (16 November 2005). "Order Lagomorpha (pp. 185-211". In Wilson, Don E., and Reeder, DeeAnn M., eds. Mammal Species of the World: A Taxonomic and Geographic Reference (3rd ed.). Baltimore: Johns Hopkins University Press, 2 vols. (2142 pp.). p. 196. ISBN 978-0-8018-8221-0. OCLC 62265494. http://www.bucknell.edu/msw3. 
  2. ^ 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. http://www.iucnredlist.org/apps/redlist/details/41276. Retrieved 01 February 2010. 
  3. ^ a b 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
  4. ^ Big Bend National Park Black-tailed Jackrabbit, US National Park Service
  5. ^ a b Flux, J. E. C. 1983. Introduction to taxonomic problems in hares. Acta Zoologica Fennica. 174: 7–10
  6. ^ Dixon, K. R. et al.. 1983. The New World jackrabbits and hares (genus Lepus).--2. Numerical taxonomic analysis. Acta Zoologica Fennica. 174: 53–56
  7. ^ 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
  8. ^ a b c d e f g h i j k l m 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
  9. ^ Hall, E. Raymond. 1951. A synopsis of the North American Lagomorpha. University of Kansas Publications, Museum of Natural History. 5(10): 119–202
  10. ^ a b c d Nydegger, Nicholas C.; Smith, Graham W. 1986. Prey populations in relation to Artemisia vegetation types in southwestern Idaho. In: McArthur, E. Durant; Welch, Bruce L., compilers. 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: 152–156
  11. ^ a b Mares, M. A.; Hulse, A. C. 1977. Patterns of some vertebrate communities in creosote bush deserts. 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: 209–226
  12. ^ a b 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
  13. ^ a b c d e f 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
  14. ^ a b c Lechleitner, R. R. 1959. Sex ratio, age classes and reproduction of the black-tailed jack rabbit. Journal of Mammalogy. 40(1): 63–81
  15. ^ a b c 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
  16. ^ a b c 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
  17. ^ a b c d e f g h i j 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
  18. ^ a b c d Smith, Graham W. 1990. Home range and activity patterns of black-tailed jackrabbits. Great Basin Naturalist. 50(3): 249–256
  19. ^ a b c 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.
  20. ^ 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
  21. ^ a b c Daniel, Alipayou et al.. 1993. Range condition influences on Chihuahuan Desert cattle and jackrabbit diets. Journal of Range Management. 46(4): 296–301
  22. ^ a b c 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
  23. ^ a b c 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
  24. ^ a b 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
  25. ^ a b 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
  26. ^ 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. 
  27. ^ 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. 
  28. ^ a b Janes, Stewart W. 1985. Habitat selection in raptorial birds. In: Cody, Martin L., ed. Habitat selection in birds. Academic Press Inc: 159–188
  29. ^ Grubb, Teryl G.; Kennedy, Charles E. 1982. Bald eagle winter habitat on southwestern National Forests. Res. Pap. RM-237. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station
  30. ^ 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
  31. ^ 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
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