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Lifespan, longevity, and ageing

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Maximum longevity: 5.8 years (captivity) Observations: One captive specimen lived 5.8 years (Richard Weigl 2005).
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Life Expectancy

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Average lifespan
Status: captivity:
5.8 years.

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Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Habitat

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The Great Basin pocket mouse can be found in shrub/grassland communities of sagebrush, shadscale, greasewood, mountain mahogany, and bitterbrush. Habitats dominated with shrub are useful in vegetative cover, while also providing better and more diverse food resources (Bushey 1987).

Terrestrial Biomes: desert or dune ; savanna or grassland

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Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Distribution

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This pocket mouse can be found in the Great Basin from South British Columbia (Canada), south to eastern California and east to southeast Wyoming and northwest Arizona (Wilson 1993).

Biogeographic Regions: nearctic (Native )

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Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Trophic Strategy

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Its diet consists mostly of seeds of forbs, grasses and shrubs. Along with green vegetation, insects are eaten particularly when they are abundant (Grzimek 1990).

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Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Conservation Status

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Great Basin pocket mice are common and not endangered (Grzimek 1990). Because they are able to retreat to underground burrows, these mice are not in much immediate danger from fires in sagebrush and bunch grass habitats. However, fires reduce food resources and vegetative cover, making the mice more susceptible to predators (Bushey 1987).

IUCN Red List of Threatened Species: least concern

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Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Behavior

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Perception Channels: tactile ; chemical

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Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Untitled

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The family name of Heteromyidae comes from the Greek "heteros", meaning "the other, different from the usual," while the genus name of Perognathus comes from two words in Greek. "Pera" means "a pouch, a pocket," and "gnathos" is "the jaw, the mouth" (Gotch 1979).

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Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Morphology

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Head and body length: 60-90 mm Tail length: 45-100 mm

The upper parts of its body are a pinkish buff color, which is thinly to heavily overlaid with a blackish color, while the underparts vary from white to buffy. The soft coat of this mouse has no bristles. One molt takes place in late summer. The soles of its hind feet are hairy, and the tail is long and bicolored (Hall 1981).

Its hind limbs are about the same length of its forelimbs, and the Great Basin pocket mouse moves about on all four legs. While the hind legs provide support, the forefeet dig with claws through sand to find seeds (Nowak 1991). These seeds are then placed in fur-lined external cheek pouches, which open alongside its mouth (Britannica 1997).

Other Physical Features: endothermic ; bilateral symmetry

Average mass: 20.1 g.

Average basal metabolic rate: 0.16 W.

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Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Reproduction

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From about late April to early August, males are in breeding condition, while females show the first sign of estrus in April. Early June is probably when breeding occurs at its peak. Pregnancies then occur from May to July. Gestation lasts 21 to 25 days. When there is an abundance of food, females have an average of two litters per year. Some have even been found to have three litters. Otherwise, an average of 1.1 litters is produced. Litters vary from three to eight mice. Juveniles born early in the season are able to breed themselves by late summer (Nowak 1991).

Key Reproductive Features: gonochoric/gonochoristic/dioecious (sexes separate); sexual

Average birth mass: 1.5 g.

Average gestation period: 24 days.

Average number of offspring: 4.8.

Average age at sexual or reproductive maturity (female)
Sex: female:
100 days.

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bibliographic citation
Luu, J. 1999. "Perognathus parvus" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Perognathus_parvus.html
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Janette Luu, University of Michigan-Ann Arbor
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Associated Plant Communities

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More info for the terms: shrub, woodland

The Great Basin pocket mouse occupies steppes and open, arid shrublands
and woodlands. It most commonly occurs in sagebrush (Artemisia spp.),
shadscale (Atriplex confertifolia), and other desert shrub, and in
pinyon-juniper (Pinus-Juniperus spp.) woodland. On the eastern slope of
the Cascade Range and the Sierra Nevada, it occurs in ponderosa pine (P.
ponderosa) and Jeffrey pine (P. jeffreyi) woodlands [18]. Riparian
zones may have larger concentrations of Great Basin pocket mice than
upland areas [8,9].
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bibliographic citation
Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Common Names

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Great Basin pocket mouse
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Conservation Status

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More info for the term: natural

The Great Basin pocket mouse has been assigned a state rank of S2* by
the Montana Natural Heritage Program [37].

*imperiled because of rarity or other factors making it very vulnerable to
extinction
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Cover Requirements

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More info for the terms: cover, torpor

Great Basin pocket mice are nocturnal and use burrows for daytime cover.
They also use burrows during periods of winter and summer torpor
[30,32,38,43]. The winter burrow consists of a 3- to 6-foot- (0.9-1.8 m-)
deep tunnel leading to a chamber lined with dry vegetation. The
summer burrow is shallow. Except for mothers with young, the burrow is
occupied by a single individual [43].
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Distribution

provided by Fire Effects Information System Animals
The Great Basin pocket mouse occurs in the Columbia River and Great
basins and adjacent lands. It is distributed from south-central British
Columbia and eastern Washington south to southeastern California,
Nevada, and northern Arizona and east to southeastern Montana and
Wyoming [3,43]. Distribution of subspecies is [18,21]:

Perognathus parvus bullatus: central and east-central Utah
P. p. clarus: extreme southwestern Montana; southeastern Idaho;
extreme north-central Utah; extreme southwestern Wyoming
P. p. columbianus: central and southern Washington
P. p. idahoensis: south-central Idaho
P. p. laingi: south-central British Columbia
P. p. lordi: extreme south-central British Columbia; central and
eastern Washington; northwestern Idaho
P. p. mollipilosus: south-central Oregon; north-central and
northeastern California
P. p. olivaceus: most of Nevada; eastern California; extreme
southeastern Oregon; southern Idaho; western Colorado; most widely
distributed subspecies
P. p. parvus: southeastern Washington; central and eastern Oregon
P. p. trumbullensis: southern Colorado; northern Arizona
P. p. yakimensis: south-central Washington

The yellow-eared pocket mouse occurs on the eastern slope of the
Tehachipi Mountains in Kern County, California [21,43]. It is not
certain whether its distribution is disjunct or joins that of P. parvus
olivaceus [18].
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Food Habits

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More info for the terms: cover, forb, seed, torpor

Great Basin pocket mice consume primarily seeds, but eat some green
vegetation [33,34]. Prior to production of seeds, they also consume
insects [11]. Great Basin pocket mice do not use free water [36]; they
metabolize water from food [43]. Pocket mice (Perognathus spp.) and
other heteromyids are scatterhoarders: They cache seeds in shallow
depressions and cover the seeds with soil. The seeds are primarily
those of grass species, and some preferred forb species. Indian
ricegrass (Oryzopsis hymenoides) [29], cheatgrass (Bromus tectorum),
Russian-thistle (Salsola kali), [38], antelope bitterbrush (Purshia
tridentata) [16,43], pigweed (Amaranthus spp.), and mustard (Brassica
spp.) [43] seeds are important Great Basin pocket mouse food items. In
productive years, cheatgrass seeds formed a major portion of the diet of
Great Basin pocket mice in southeastern Washington [38].

Seeds of medusahead (Taeniatherum caput-medusae) were not used by Great
Basin pocket mice in Lassen County, California, and areas with heavy
medusahead invasion were avoided [29].

Estimated seed intake of a Great Basin pocket mouse is from 4 to 10
percent of total body weight daily. Assuming a wholly cheatgrass diet,
an individual requires 870 to 1,000 seeds per day in spring and summer,
and about 750 seeds per day in fall. Estimated daily maintenance energy
requirement ranges from a winter low of 2.4 kilocalories (males) and 2.6
kilocalories (females) to a high of 7.0 kilocalories (males) and 6.6
kilocalories (females) in spring. A total of about 1.8 to 2.1 ounces
(50-60 g) of seed must be cached to meet the winter energy requirement
[38]. To conserve energy when food is scarce in summer, Great Basin
pocket mice often enter a state of torpor that lasts a few hours
[23,38].

Great Basin pocket mice are fairly successful at finding buried seed
caches, even those buried by other individuals. In a laboratory
experiment, Great Basin pocket mice found Indian ricegrass seeds 17.5
percent of the time when researchers cached seeds 1.3 centimeters below
ground; 42.5 percent of the time when seeds were cached 0.6 centimeter
below ground; and 100 percent of the time when seeds were scattered on
the soil surface [25].
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Cover Types

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This species is known to occur in association with the following cover types (as classified by the Society of American Foresters):

237 Interior ponderosa pine
238 Western juniper
239 Pinyon-juniper
247 Jeffrey pine
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Ecosystem

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This species is known to occur in the following ecosystem types (as named by the U.S. Forest Service in their Forest and Range Ecosystem [FRES] Type classification):

More info for the term: shrub

FRES21 Ponderosa pine
FRES29 Sagebrush
FRES30 Desert shrub
FRES34 Chaparral-mountain shrub
FRES35 Pinyon-juniper
FRES36 Mountain grasslands
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Plant Associations

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This species is known to occur in association with the following plant community types (as classified by Küchler 1964):

More info for the terms: forest, shrub, woodland

K010 Ponderosa shrub forest
K011 Western ponderosa forest
K023 Juniper-pinyon woodland
K034 Montane chaparral
K038 Great Basin sagebrush
K040 Saltbush-greasewood
K041 Creosotebush
K050 Fescue-wheatgrass
K051 Wheatgrass-bluegrass
K055 Sagebrush steppe
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Rangeland Cover Types

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This species is known to occur in association with the following Rangeland Cover Types (as classified by the Society for Range Management, SRM):

More info for the terms: shrub, shrubland, woodland

101 Bluebunch wheatgrass
102 Idaho fescue
104 Antelope bitterbrush-bluebunch wheatgrass
105 Antelope bitterbrush-Idaho fescue
106 Bluegrass scabland
107 Western juniper/big sagebrush/bluebunch wheatgrass
109 Ponderosa pine shrubland
110 Ponderosa pine-grassland
210 Bitterbrush
211 Creosotebush scrub
212 Blackbush
301 Bluebunch wheatgrass-blue grama
302 Bluebunch wheatgrass-Sandberg bluegrass
303 Bluebunch wheatgrass-western wheatgrass
304 Idaho fescue-bluebunch wheatgrass
305 Idaho fescue-Richardson needlegrass
306 Idaho fescue-slender wheatgrass
307 Idaho fescue-threadleaf sedge
309 Idaho fescue-western wheatgrass
311 Rough fescue-bluebunch wheatgrass
312 Rough fescue-Idaho fescue
314 Big sagebrush-bluebunch wheatgrass
315 Big sagebrush-Idaho fescue
316 Big sagebrush-rough fescue
317 Bitterbrush-bluebunch wheatgrass
318 Bitterbrush-Idaho fescue
320 Black sagebrush-bluebunch wheatgrass
321 Black sagebrush-Idaho fescue
323 Shrubby cinquefoil-rough fescue
401 Basin big sagebrush
402 Mountain big sagebrush
403 Wyoming big sagebrush
405 Black sagebrush
406 Low sagebrush
407 Stiff sagebrush
408 Other sagebrush types
412 Juniper-pinyon woodland
413 Gambel oak
414 Salt desert shrub
501 Saltbush-greasewood
506 Creosotebush-bursage
504 Juniper-pinyon pine woodland
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Management Considerations

provided by Fire Effects Information System Animals
More info for the terms: competition, forest, herbaceous, seed

As scatterhoarders, Great Basin pocket mice and other heteromyids have
great ecological importance. Some native desert plant species including
Indian ricegrass, antelope bitterbrush, and palo verde (Cercidium
microphyllum) have no seed appendages to facilitate dispersal, and
apparently require heteromyids for seed dispersal [29]. Many seed
caches of these granivores are not consumed, and unconsumed seed in
caches has a greater probability of germinating and establishing than
does uncached seed. McAdoo and Klebenow [32] found that Indian
ricegrass seeds from scatterhoards often had 100 percent germination.
This is probably because only seeds with filled seedcoats were cached,
and because seedcoats are often cracked and embryos germinate more
easily when seeds are handled by heteromyids. Furthermore,
scatterhoards are not vulnerable to bird and ant granivores [29].

Schreiber [38] concluded that Great Basin pocket mice probably do not
reduce cheatgrass importance in southeastern Washington even though they
consume large numbers of cheatgrass seeds. Surviving cheatgrass plants
have reduced competition for soil nutrients and water, and respond with
increased seed production.

Disturbance tends to favor Great Basin pocket mice, especially when the
disturbance favors growth of herbaceous species. In Oregon, Great Basin
pocket mouse populations were greater in logged than in unlogged forest
[4]. In southern Utah, populations were larger in pinyon-juniper
(Pinus-Juniperus spp.) chained and seeded to grasses than in untreated
pinyon-juniper [1]. Grass seeding attracts Great Basin pocket mice to
scattered seed and later, to new herbaceous growth [2].

Light- to moderate-intensity livestock grazing apparently does not
reduce Great Basin pocket mouse numbers. In Nevada, populations were
actually larger in riparian zones grazed by cattle than in ungrazed
riparian zones [9]. In northwestern Nevada, Oldemeyer and Allen-Johnson
[35] found no significant differences between in Great Basin pocket
mouse abundance on ungrazed sites and on an allotment subjected to
a light-to-moderate-use deferred grazing system.
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Occurrence in North America

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AZ
CA
CO
ID
MT
NV
OR
UT
WA
WY





BC

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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Predators

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Owls (Tytonidae and Strigidae) [43], including northern saw-whet owls
(Aegolius acadicus) [8] and burrowing owls (Speotyto cunicularia) [24],
hawks (Accipitridae) [43], coyotes (Canis latrans) [12,40], foxes (Vulpes
and Urocyon spp.), weasels and skunks (Mustelidae), and snakes
(Serpentes) [43] prey on Great Basin pocket mice.
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Preferred Habitat

provided by Fire Effects Information System Animals
Great Basin pocket mice occupy open, arid terrain. They seek friable
soil of a variety of textures for burrowing [5,22,42].

Home ranges of 7,060 to 9,630 square feet (656-895 sq m) have been
reported for Great Basin pocket mice in British Columbia. Males may
have larger home ranges than females. Average home ranges reported from
south-central Washington are 23,030 square feet (2,140 sq m) and 33,640
square feet (3,125 sq m) for adult males and 15,564 square feet (1,446
sq m) for adult females [38]. In big sagebrush habitat on the Malheur
National Wildlife Refuge, Oregon, home ranges of adult males were
significantly greater (p < 0.001) than home ranges of females.
Reproductively active adult males had significantly (p < 0.05) larger
home ranges than adult males with unenlarged testes. In black
greasewood (Sarcobatus vermiculatus) habitat, however, there were no
significant differences between male and female home ranges or between
home ranges of reproductive and nonreproductive adult males [14].
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Regional Distribution in the Western United States

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More info on this topic.

This species can be found in the following regions of the western United States (according to the Bureau of Land Management classification of Physiographic Regions of the western United States):

5 Columbia Plateau
6 Upper Basin and Range
7 Lower Basin and Range
8 Northern Rocky Mountains
9 Middle Rocky Mountains
10 Wyoming Basin
12 Colorado Plateau
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Taxonomy

provided by Fire Effects Information System Animals
The scientific name of the Great Basin pocket mouse is Perognathus
parvus (Peale). It is in the family Heteromyidae [18,19,21,26].
Subspecies of the Great Basin pocket mouse are:

Perognathus parvus bullatus Durrant and Lee
Perognathus parvus clarus Goldman
Perognathus parvus columbianus Merriam
Perognathus parvus idahoensis Goldman
Perognathus parvus laingi Anderson
Perognathus parvus lordi (Gray)
Perognathus parvus mollipilosus Coues [18,21]
Perognathus parvus olivaceus Merriam
Perognathus parvus parvus (Peale) [21]
Perognathus parvus trumbullensis Benson
Perognathus parvus yakimensis Broadbooks [18,21]

Sulentich [41] and Genoways and Brown [18] classify the yellow-eared
pocket mouse as P. p. xanthonus Grinell, a subspecies of the Great
pocket mouse. However, Jones and others [26] classify the yellow-eared
pocket mouse as a distinct species, P. xanthonotus (Grinnell).
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bibliographic citation
Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Timing of Major Life History Events

provided by Fire Effects Information System Animals
More info for the terms: litter, torpor

In late fall and winter, Great Basin pocket mice remain in their burrows
in a state of torpor [33,34]. They emerge from their burrows and mate
in early spring [33,34,43]. Males emerge slightly before females. In
south-central Washington, Great Basin pocket mice emerged from March to
April [23]. Prebreeding enlargement of ovaries and testes begins in
winter in the complete darkness of the burrow. Following emergence from
the burrow, the lengthening photoperiod of spring apparently triggers
final enlargement and development of gonads for breeding [27]. Access
to succulent green vegetation in spring may enhance reproductive success
of females. Captive female Great Basin pocket mice from eastern
Washington fed lettuce and seeds had significantly larger ovaries than
control females fed only seeds. Great Basin pocket mice remain
reproductively active through summer. Females produce one or two
litters per year. Most first litters are delivered in May and second
litters in August [38,43]. Reports of average litter size have ranged
from 3.9 in south-central Washington [38] to 5.6 in Nevada [20].
First-litter subadults first leave the natal burrow in early summer;
subadults from the second litter first emerge in fall. In a 2-year
study in south-central Washington, first-litter subadults first emerged
in June, and second-litter subadults first emerged in October (1974) and
November (1975) [23].

As it signals the beginning of the breeding season, photoperiod may
often signal its end. In the laboratory, an artificial short day-long
night summer photoperiod caused gonadal shrinkage in Great Basin pocket
mice. A favorable diet apparently overrides this effect, however,
extending the breeding season. In nature, Great Basin pocket mice
remain reproductively active through fall in years of favorable plant
production. Juveniles typically breed in their second year, but
first-litter individuals may first reach breeding condition before
winter when plant productivity is high [27].
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Howard, Janet L. 1996. Perognathus parvus. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Great Basin pocket mouse

provided by wikipedia EN

The Great Basin pocket mouse (Perognathus parvus) is a species of rodent in the family Heteromyidae.[2][3][4][5] It is found in British Columbia in Canada and the western United States.[1]

Taxonomy

There are several subspecies of P. parvus. Sulentich[6] and Genoways and Brown[2] classify the yellow-eared pocket mouse as P. p. xanthonus Grinell, a subspecies of the Great Basin pocket mouse. However, Jones and others[4] classify the yellow-eared pocket mouse as a distinct species, P. xanthonotus (Grinnell).

Distribution

The Great Basin pocket mouse occurs in the Columbia River Basin and the Great Basin and adjacent lands. It is distributed from south-central British Columbia and eastern Washington south to southeastern California, Nevada and northern Arizona, and east to southeastern Montana and Wyoming.[7][8] Distribution of subspecies is:[2][3]

  • Perognathus parvus bullatus: (Durrant and Lee) – central and east-central Utah
  • P. p. clarus (Goldman) – extreme southwestern Montana; southeastern Idaho; extreme north-central Utah; extreme southwestern Wyoming
  • P. p. columbianus (Merriam) – central and southern Washington
  • P. p. idahoensis (Goldman) – south-central Idaho
  • P. p. laingi (Anderson) – south-central British Columbia
  • P. p. lordi (Gray) – extreme south-central British Columbia; central and eastern Washington; northwestern Idaho
  • P. p. mollipilosus (Coues)[2][3] – south-central Oregon; north-central and northeastern California
  • P. p. olivaceus (Merriam) – most of Nevada; eastern California; extreme southeastern Oregon; southern Idaho; western Colorado; the most widely distributed subspecies
  • P. p. parvus (Peale)[3] – southeastern Washington; central and eastern Oregon
  • P. p. trumbullensis (Benson) – southern Colorado; northern Arizona
  • P. p. yakimensis (Broadbooks)[2][3] – south-central Washington

The yellow-eared pocket mouse occurs on the eastern slope of the Tehachapi Mountains in Kern County, California.[3][8] It is not certain whether its distribution is disjunct or joins that of P. parvus olivaceus.[2]

Plant communities

The Great Basin pocket mouse occupies steppes and open, arid shrublands and woodlands. It most commonly occurs in sagebrush (Artemisia spp.), shadscale (Atriplex confertifolia), and other desert shrublands, and in pinyon-juniper (Pinus-Juniperus spp.) woodland. On the eastern slope of the Cascade Range and the Sierra Nevada, it occurs in ponderosa pine (P. ponderosa) and Jeffrey pine (P. jefferyi) woodlands.[2] Riparian zones may have larger concentrations of Great Basin pocket mice than upland areas.[9][10]

Timing of major life events

In late fall and winter, Great Basin pocket mice remain in their burrows in a state of torpor.[11][12] They emerge from their burrows and mate in early spring.[8][11][12] Males emerge slightly before females. In south-central Washington, Great Basin pocket mice emerged from March to April.[13] Prebreeding enlargement of ovaries and testes begins in winter in the complete darkness of the burrow. Following emergence from the burrow, the lengthening photoperiod of spring apparently triggers final enlargement and development of gonads for breeding.[14] Access to succulent green vegetation in spring may enhance reproductive success of females. Captive female Great Basin pocket mice from eastern Washington fed lettuce and seeds had significantly larger ovaries than control females fed only seeds. Great Basin pocket mice remain reproductively active through summer. Females produce one or two litters per year. Most first litters are delivered in May and second litters in August.[8][15] Reports of average litter size have ranged from 3.9 in south-central Washington[15] to 5.6 in Nevada.[16] First-litter subadults first leave the natal burrow in early summer; subadults from the second litter first emerge in fall. In a 2-year study in south-central Washington, first-litter subadults first emerged in June, and second-litter subadults first emerged in October (1974) and November (1975).[13]

As it signals the beginning of the breeding season, photoperiod may often signal its end. In the laboratory, an artificial short day-long night summer photoperiod caused gonadal shrinkage in Great Basin pocket mice. A favorable diet apparently overrides this effect, however, extending the breeding season. In nature, Great Basin pocket mice remain reproductively active through fall in years of favorable plant production. Juveniles typically breed in their second year, but first-litter individuals may first reach breeding condition before winter when plant productivity is high.[14]

Great Basin pocket mice occupy open, arid terrain. They seek friable soil of a variety of textures for burrowing.[17][18][19]

Home ranges of 7,060 to 9,630 square feet (656–895 sq m) have been reported for Great Basin pocket mice in British Columbia. Males may have larger home ranges than females. Average home ranges reported from south-central Washington are 23,030 square feet (2,140 sq m) and 33,640 square feet (3,125 sq m) for adult males and 15,564 square feet (1,446 sq m) for adult females.[15] In big sagebrush habitat on the Malheur National Wildlife Refuge, Oregon, home ranges of adult males were significantly greater (p < 0.001) than home ranges of females. Reproductively active adult males had significantly (p < 0.05) larger home ranges than adult males with unenlarged testes. In black greasewood (Sarcobatus vermiculatus) habitat, however, there were no significant differences between male and female home ranges or between home ranges of reproductive and nonreproductive adult males.[20]

Cover requirements

Great Basin pocket mice are nocturnal and use burrows for daytime cover. They also use burrows during periods of winter and summer torpor.[8][15][21][22] The winter burrow consists of a 3- to 6-foot- (0.9–1.8 m-) deep tunnel leading to a chamber lined with dry vegetation. The summer burrow is shallow. Except for mothers with young, the burrow is occupied by a single individual.[8]

Food habits

Great Basin pocket mice consume primarily seeds, but eat some green vegetation.[11][12] Prior to production of seeds, they also consume insects.[23] Great Basin pocket mice do not use free water,[24] they metabolize water from food.[8] Pocket mice (Perognathus spp.) and other heteromyids are scatterhoarders, caching seeds in shallow depressions and covering the seeds with soil. The seeds are primarily those of grass species, and some preferred forb species. Indian ricegrass (Oryzopsis hymenoides),[25] cheatgrass (Bromus tectorum), Russian-thistle (Salsola kali),[15] antelope bitterbrush (Purshia tridentata), pigweed (Amaranthus spp.), and mustard (Brassica spp.)[8] seeds are important Great Basin pocket mouse food items. In productive years, cheatgrass seeds formed a major portion of the diet of Great Basin pocket mice in southeastern Washington.[15]

Seeds of medusahead (Taeniatherum caput-medusae) were not used by Great Basin pocket mice in Lassen County, California, and areas with heavy medusahead invasion were avoided.[25]

Estimated seed intake of a Great Basin pocket mouse is from 4% to 10% of total body weight daily. Assuming a wholly cheatgrass diet, an individual requires 870 to 1,000 seeds per day in spring and summer, and about 750 seeds per day in fall. Estimated daily maintenance energy requirement ranges from a winter low of 2.4 kilocalories (males) and 2.6 kilocalories (females) to a high of 7.0 kilocalories (males) and 6.6 kilocalories (females) in spring. A total of about 1.8 to 2.1 ounces (50–60 g) of seed must be cached to meet the winter energy requirement.[15] To conserve energy when food is scarce in summer, Great Basin pocket mice often enter a state of torpor that lasts a few hours.[13][15]

Great Basin pocket mice are fairly successful at finding buried seed caches, even those buried by other individuals. In a laboratory experiment, Great Basin pocket mice found Indian ricegrass seeds 17.5% of the time when researchers cached seeds 1.3 centimeters below ground; 42.5% of the time when seeds were cached 0.6 centimeter below ground; and 100% of the time when seeds were scattered on the soil surface.[26]

Predators

Owls (Tytonidae and Strigidae),[8] including northern saw-whet owls (Aegolius acadicus)[9] and burrowing owls (Speotyto cunicularia)[27] hawks (Accipitridae),[8] coyotes (Canis latrans),[28][29] foxes (Vulpes and Urocyon spp.), weasels and skunks (Mustelidae), and snakes[8] prey on Great Basin pocket mice.

References

Public Domain This article incorporates public domain material from Perognathus parvus. United States Department of Agriculture.

  1. ^ a b c Linzey, A.V. & Hammerson, G. (NatureServe) (2008). "Perognathus parvus". IUCN Red List of Threatened Species. 2008. Retrieved 22 January 2009.old-form url Database entry includes a brief justification of why this species is of least concern
  2. ^ a b c d e f g Williams, Daniel F.; Genoways, Hugh H.; Braun, Janet K. 1993. Taxonomy. In: Genoways, Hugh H.; Brown, James H. (eds.) Biology of the Heteromyidae. Special Publication No. 10. The American Society of Mammalogists: 38–196
  3. ^ a b c d e f Hall, E. Raymond. 1981. The mammals of North America. 2nd ed. Volume I. New York: John Wiley & Sons
  4. ^ a b Jones, J. Knox, Jr.; Hoffmann, Robert S.; Rice, Dale W.; 1992. Revised checklist of North American mammals north of Mexico, 1991. Occasional Papers No. 146. Lubbock, TX: Texas Tech University, The Museum.
  5. ^ Hafner, John C.; Hafner, Mark S. (1983). "Evolutionary relationships of Heteromyid rodents". Great Basin Naturalist. 7: 3–29.
  6. ^ Sulentich, J. M. 1983. The systematics and evolution of the Perognathus parvus species group in southern California. Long Beach, CA: California State University.
  7. ^ 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
  8. ^ a b c d e f g h i j k Whitaker, John O. Jr. (1980). National Audubon Society field guide to North American mammals. New York: Alfred A. Knopf, Inc. ISBN 0394507630
  9. ^ a b Cannings, Richard J. 1987. The breeding biology of northern saw-whet owls in southern British Columbia. In: Nero, Robert W.; Clark, Richard J.; Knapton, Richard J.; Hamre, R. H., eds. Biology and conservation of northern forest owls: Symposium proceedings; 1987 February 3–7; Winnipeg, MB. Gen. Tech. Rep. RM-142. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 193–198.
  10. ^ Clary, Warren P.; Medin, Dean E. 1992. Vegetation, breeding bird, and small mammal biomass in two high-elevation sagebrush riparian habitats. In: Clary, Warren P.; McArthur, E. Durant; Bedunah, Don; Wambolt, Carl L., compilers. Proceedings—symposium on ecology and management of riparian shrub communities; 1991 May 29–31; Sun Valley, ID. Gen. Tech. Rep. INT-289. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 100–110
  11. ^ a b c O'Farrell, Michael J. (1978). "Home range dynamics of rodents in a sagebrush community". Journal of Mammalogy. 59 (4): 657–668. doi:10.2307/1380131. JSTOR 1380131.
  12. ^ a b c O'Farrell, Thomas P.; Olson, Richard J.; Gilbert, Richard O.; Hedlund, John D. (1975). "A population of Great Basin pocket mice, Perognathus parvus, in the shrub-steppe of south-central Washington". Ecological Monographs. 45 (1): 1–28. doi:10.2307/1942329. JSTOR 1942329.
  13. ^ a b c Hedlund, J. D.; Rogers, L. E. (1980). "Great Basin pocket mice (Perognathus parvus) in the vicinity of radioactive waste management areas" (PDF). Northwest Science. 54 (2): 153–159. Archived from the original (PDF) on 2011-06-10. Retrieved 2010-07-21.
  14. ^ a b Kenagy, G. J.; Barnes, B. M. (1984). "Environmental and endogenous control of reproductive function in the Great Basin pocket mouse Perognathus parvus". Biology of Reproduction. 31 (4): 637–645. doi:10.1095/biolreprod31.4.637. PMID 6509135.
  15. ^ a b c d e f g h Schreiber, R. Kent (1978). "Bioengergetics of the Great Basin pocket mouse, Perognathus parvus". Acta Theriologica. 23 (32): 469–487. doi:10.4098/at.arch.78-38.
  16. ^ Hall, E. Raymond. 1946. Mammals of Nevada. Berkeley, CA: University of California Press
  17. ^ Black, Hal L.; Frischknecht, Neil C. 1971. Relative abundance of mice on seeded sagebrush-grass range in relation to grazing. Res. Note INT-147. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station
  18. ^ Hedlund, J. D.; Rickard, W. H. (1981). "Wildfire and the short-term response of small mammals inhabiting a sagebrush-bunchgrass community". Murrelet. 62 (1): 10–14. doi:10.2307/3534441. JSTOR 3534441.
  19. ^ 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
  20. ^ Feldhamer, George A. (1979). "Home range relationships of three rodent species in southeast Oregon". Murrelet. 60 (2): 50–57. doi:10.2307/3535769. JSTOR 3535769.
  21. ^ Maser, Chris; Thomas, Jack Ward; Anderson, Ralph G. 1984. Wildlife habitats in managed rangelands—the Great Basin of southeastern Oregon: The relat. of terrestrial vertebrates to plant communities: Part 2. Appendices. Gen. Tech. Rep. PNW-172. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station; Washington, DC: U.S. Department of the Interior, Bureau of Land Management
  22. ^ McAdoo, J. Kent; Klebenow, Donald A. 1979. Native faunal relationships in sagebrush ecosystems. In: The sagebrush ecosystem: a symposium: Proceedings; 1978 April; Logan, UT. Logan, UT: Utah State University, College of Natural Resources: 50–61
  23. ^ Dunigan, P. F. X. Jr.; Lei, W.; Rickard, W. H. (1980). "Pocket mouse population response to winter precipitation and drought" (PDF). Northwest Science. 54 (4): 289–295.
  24. ^ Price, M. V.; Brown, J. H. (1983). "Patterns of morphology and resource use in North American desert rodent communities". Great Basin Naturalist Memoirs. 7: 117–134.
  25. ^ a b Longland, William S. 1994. Seed use by desert granivores. In: Monsen, Stephen B.; Kitchen, Stanley G., compilers. Proceedings—ecology and management of annual rangelands; 1992 May 18–22; Boise, ID. Gen. Tech. Rep. INT-GTR-313. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 233–237
  26. ^ Johnson, Terrell K.; Jorgensen, Clive D. (1981). "Ability of desert rodents to find buried seeds". Journal of Range Management. 34 (4): 312–314. doi:10.2307/3897858. hdl:10150/646129. JSTOR 3897858. Archived from the original on 2013-04-09. Retrieved 2013-03-17.
  27. ^ Henny, Charles J.; Blus, Lawrence J. (1981). "Artificial burrows provide new insight into burrowing owl nesting biology" (PDF). Raptor Research. 15 (3): 82–85.
  28. ^ Edwards, Loren Lee. 1975. Home range of the coyote in southern Idaho. Pocatello, ID: Idaho State University, Thesis
  29. ^ Springer, Joseph Tucker (1982). "Movement patterns of coyotes in south central Washington". Journal of Wildlife Management. 46 (1): 191–200. doi:10.2307/3808422. JSTOR 3808422.
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Great Basin pocket mouse: Brief Summary

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The Great Basin pocket mouse (Perognathus parvus) is a species of rodent in the family Heteromyidae. It is found in British Columbia in Canada and the western United States.

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