Vulpes macrotis mutica

Merriam, 1902

Kit Fox - San Joaquin Valley Population

T2T2 (G4T2) Found in 23 roadless areas NatureServe Explorer →
T2T2Global Rank
High - mediumThreat Impact
San Joaquin kit fox (Vulpes macrotis mutica). Photo by U.S. Fish & Wildlife Service, Public Domain (U.S. Government Work), via ECOS.
U.S. Fish & Wildlife Service, https://www.usa.gov/government-works
Identity
Unique IDELEMENT_GLOBAL.2.101320
Element CodeAMAJA03041
Record TypeSPECIES
ClassificationSubspecies
Classification StatusStandard
Name CategoryVertebrate Animal
Endemicendemic to a single state or province
KingdomAnimalia
PhylumCraniata
ClassMammalia
OrderCarnivora
FamilyCanidae
GenusVulpes
Other Common Names
San Joaquin kit fox (EN)
Concept Reference
Wilson, D. E., and D. M. Reeder (editors). 1993. Mammal species of the world: a taxonomic and geographic reference. Second edition. Smithsonian Institution Press, Washington, DC. xviii + 1206 pp. Available online at: http://www.nmnh.si.edu/msw/.
Conservation Status
Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2013-03-13
Change Date2013-03-13
Edition Date2013-03-13
Edition AuthorsHammerson, G.
Threat ImpactHigh - medium
Range Extent20,000-200,000 square km (about 8000-80,000 square miles)
Number of Occurrences6 - 20
Rank Reasons
Reduced, fragmented range in the San Joaquin Valley and adjacent areas in California, population size probably a few to several thousand individuals; declining due to habitat loss/degradation/fragmentation caused by human activities, interactions with coyotes and red foxes, poisoning efforts that have reduced prey populations, and other factors.
Range Extent Comments
Range includes the San Joaquin Valley, California, encompassing portions of the valley floor and adjacent foothills and interior Coast Range valleys, historically from as far north as Tracy (San Joaquin County) and La Grange (Stanislaus County) and south to Kern County) (Grinnell et al. 1937, USFWS 2010). At one time, the range was believed to have decreased to only the southern and western parts of the San Joaquin Valley and adjacent foothills and interior Coast Range Valleys, but subsequent research found these foxes in many additional areas, northward to Contra Costa County, including areas where the species previously had not been detected (USFWS 2010). However, some recently documented locations likely reflect dispersing individuals rather than resident populations, and many populations are small, isolated, and/or declining or apparently extirpated (USFWS 2010).
Occurrences Comments
This fox is represented by three core subpopulation units and several satellite subpopulations (USFWS 2010).
Threat Impact Comments
Decline is attributable to conversion of habitat to irrigated cropland; residential, water, and petroleum development, and poisoning programs that have reduced prey populations (Biosystems Analysis 1989, California DF&G 1990). Interactions with coyotes (predation, competition) can have a significant negative impact on populations (see USFWS 2010), and expanding populations of non-native red foxes may pose a threat in some areas (see USFWS 2010).

USFWS (2010) summarized threats to habitat as follows: Loss, modification, and fragmentation of habitat continue to be the primary threats. Most of the optimal habitat on the valley floor has been converted to agriculture. Although the rate of agricultural conversion on the valley floor has slowed in recent years, urban and agricultural conversion activities have continued to extend up to and into the lower foothill slopes where corridors of residual habitat had remained. In many areas, remaining natural lands have become fragmented, inhibiting movement of kit fox between remnant parcels and delaying or preventing recolonization of retired and restored habitat. Some isolated parcels, including protected lands, have lost the vegetative structure or prey species important to persistence of kit fox populations, resulting in loss of resident kit fox subpopulations. Restoration of the kit fox's natural habitat has proved difficult, and lands, such as retired lands that were thought to be valuable for kit fox recovery, do not necessarily provide adequate conditions for kit fox. In the Western Kern County and the Carrizo Plain core areas, where foxes remain relatively abundant, threats due to oil and gas leasing continue. USFWS and its public and private partners have made great progress in acquiring lands for conservation. Currently, land ownership or management for 60 percent of occurrences is unknown, 13 percent of occurrences are recorded from private lands, and roughly 24 percent of occurrences are recorded from various federal, state, regional, county, and city holdings that are subject to varying management goals and objectives. Kit foxes are mobile predators that require large home ranges, and appropriate vegetative, prey, and predator conditions to persist. Despite recent conservation efforts, kit fox subpopulations appear to be declining.

A number of large-scale solar development projects that would threaten kit fox population clusters are
currently proposed for construction in kit fox habitat (USFWS 2010).

Constriction of available habitat and occurrence of barriers such as the canals and several high-traffic roads potentially limit fox movements (see USFWS 2010).

USFWS (2010) summarized the threat from predation and disease as follows. Predation by large canid predators including the coyote and non-native red fox appears to be a major and increasing threat to the viability of kit fox populations. In most areas of the kit fox's range, coyotes are the primary cause of kit fox mortality, and survival rates of kit fox decrease significantly as coyote-caused mortality increases. Canid predators have increased both in distribution and abundance with the increased land conversion, presence of water sources, and related human activities in the San Joaquin Valley. Abundant coyote populations currently appear to be excluding kit fox from some protected kit fox habitat. Disease does not appear to be an important threat to the kit fox at this time.

USFWS (2010) summarized additional threats as follows. Newer formulations of rodenticides and pesticides subject kit foxes to direct and secondary poisoning, have been linked to kit fox mortality, and are used widely within the range of the kit fox. Although no research to date has quantified the effect of rodenticides on kit fox populations, USFWS expects that rodenticide exposure could have substantial population-level effects, especially where population are small and where kit fox rely on rodent species targeted by rodenticides. The effectiveness of new regulations on the use of rodenticides in preventing kit fox exposure in not currently known. Rodenticides and pesticides may also negatively effect kit fox populations through their reduction of the fox's rodent and insect prey resources. In addition, selenium toxicity may threaten kit fox in some areas on the western side of the San Joaquin Valley where elevated concentrations of selenium are present at the ground surface. Toxicity effects range from reduced appetite and subnormal growth to mortality. Additional threats include loss of individuals to mortality from accidental shooting, vehicle strikes, off-road vehicle use, and research-related activities. Where populations are small, such events could have population-level effects and could increase the threat of stochastic extinction. Where populations are small, inbreeding depression, genetic drift, and stochastic extinction are recognized threats. Climate change may threaten kit fox populations through increased variability in precipitation and severe weather events, which in turn are expected to reduce prey availability.
Ecology & Habitat

Habitat

Habitat includes alkali sink, valley grassland, and woodland, in valleys and adjacent gentle foothills (USFWS 2010). These foxes hunt in areas with low sparse vegetation that allows good visibility and mobility (Biosystems Analysis 1989). Multiple underground dens in dry soils are used throughout the year. Sometimes these foxes use pipes or culverts as den sites (Biosystems Analysis 1989). Young are born in an underground den. Dens usually have multiple entrances.

Ecology

Density averages around 1 fox per 259 ha (California Department of Fish and Game 1990).

Annual survival rate is 0.40-0.68 in adults, 0.21-0.41 in juveniles (see Ralls and White 1995). Does not avoid coyotes; may coexist by exploiting certain prey species better than coyotes and maintaining numerous dens throughout the home range to facilitate escape (White et al. 1994).

Reproduction

Mating occurs in winter; 4-7 young are born in February or March (Biosystems Analysis 1989). Some yearling females produce young, but most do not reproduce until 2 years of age. Young generally disperse in August or September, when 4 or 5 months old. Reproductive success appears to be correlated with prey abundance. See USFWS (2010).
Terrestrial Habitats
Woodland - ConiferWoodland - MixedShrubland/chaparralSavannaGrassland/herbaceousDesertPlaya/salt flat
Other Nations (1)
United StatesN2
ProvinceRankNative
CaliforniaS3Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentRestricted - smallExtreme or 71-100% pop. declineHigh (continuing)
1.1 - Housing & urban areasRestricted - smallExtreme or 71-100% pop. declineHigh (continuing)
2 - Agriculture & aquacultureRestricted - smallExtreme - seriousHigh (continuing)
2.1 - Annual & perennial non-timber cropsExtreme - seriousHigh (continuing)
3 - Energy production & miningRestricted - smallSerious - moderateHigh (continuing)
3.1 - Oil & gas drillingUnknownModerate - slightHigh (continuing)
3.3 - Renewable energy
4 - Transportation & service corridorsRestricted - smallModerate - slightHigh (continuing)
7 - Natural system modificationsUnknownUnknownHigh (continuing)
7.2 - Dams & water management/useUnknownUnknownHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesRestricted - smallExtreme - moderateHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesExtreme - moderateHigh (continuing)
8.2 - Problematic native species/diseasesExtreme - moderateHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)Slight or 1-10% pop. declineHigh - moderate
11.2 - Droughts

Roadless Areas (23)
California (23)
AreaForestAcres
AntimonyLos Padres National Forest40,911
Bear MountainLos Padres National Forest913
Big RocksLos Padres National Forest11,866
Black MountainLos Padres National Forest16,818
Black Mtn.Sequoia National Forest15,102
CuyamaLos Padres National Forest19,631
Fox MountainLos Padres National Forest52,072
Garcia MountainLos Padres National Forest7,850
Greenhorn CreekSequoia National Forest28,226
Horseshoe SpringsLos Padres National Forest14,089
La BreaLos Padres National Forest14,031
La PanzaLos Padres National Forest4,954
Los Machos HillsLos Padres National Forest11,112
Lpoor CanyonLos Padres National Forest13,762
Machesna MountainLos Padres National Forest12,271
Mill CreekSequoia National Forest27,643
Mirada PimeLos Padres National Forest13,302
MosesSequoia National Forest22,077
QuatalLos Padres National Forest7,253
Sawmill - BadlandsLos Padres National Forest51,362
Sespe - FrazierLos Padres National Forest106,910
Stanley MountainLos Padres National Forest14,674
WoolstaffSequoia National Forest41,445
References (16)
  1. Biosystems Analysis, Inc. 1989. Endangered Species Alert Program Manual: Species Accounts and Procedures. Southern California Edison Environmental Affairs Division.
  2. California Department of Fish and Game (CDF&G). 1990. 1989 annual report on the status of California's state listed threatened and endangered plants and animals. 188 pp.
  3. Dragoo, J. W., et al. 1990. Evolutionary and taxonomic relationships among North American arid-land foxes. J. Mammalogy 71:318-332.
  4. Ingles, L. G. 1965. Mammals of the Pacific States. Stanford University Press, Stanford, California.
  5. Matthews, J.R. and C.J. Moseley (eds.). 1990. The Official World Wildlife Fund Guide to Endangered Species of North America. Volume 1. Plants, Mammals. xxiii + pp 1-560 + 33 pp. appendix + 6 pp. glossary + 16 pp. index. Volume 2. Birds, Reptiles, Amphibians, Fishes, Mussels, Crustaceans, Snails, Insects, and Arachnids. xiii + pp. 561-1180. Beacham Publications, Inc., Washington, D.C.
  6. Mercure, A., et al. 1993. Genetic subdivisions among small canids: mitochondrial DNA differentiation of swift, kit, and arctic foxes. Evolution 47:1313-1328.
  7. Morrell, S. H. 1972. Life history of the San Joaquin kit fox. California Fish and Game 58:162-174.
  8. Otten, M.R.M., and B. L. Cypher. 1998. Variation in annual estimates of effective population size for San Joaquin kit foxes. American Conservation 1:179-184.
  9. Ralls, K., and L. Eberhardt. 1997. Assessment of abundance of San Joaquin kit foxes by spotlight surveys. Journal of Mammalogy 78:65-
  10. Ralls, K., and P. J. White. 1995. Predation on San Joaquin kits foxes by larger canids. Journal of Mammalogy 76:723-729.
  11. Smith, D. A., K. Ralls, B. L. Cypher, H. O. Clark, P. A. Kelly, D. F. Williams, and J. E. Maldonado. 2006. Relative abundance of endangered San Joaquin kit foxes (<i>Vulpes macrotis mutica</i>) based on scat-detection dog surveys. Southwestern Naturalist 51: 210-219.
  12. U.S. Fish and Wildlife Service (USFWS). 1990. Endangered and threatened species recovery program: report to Congress. 406 pp.
  13. U.S. Fish and Wildlife Service (USFWS). 1998. Recovery plan for upland species of the San Joaquin Valley, California. USFWS, Portland, Oregon.
  14. U.S. Fish and Wildlife Service (USFWS). 2010. San Joaquin kit fox (<i>Vulpes macrotis mutica</i>) 5-year review: summary and evaluation. USFWS, Sacramento Fish and Wildlife Office, Sacramento, California.
  15. White, P. J., K. Ralls, and R. A. Garrott. 1994. Coyote-kit fox interactions as revealed by telemetry. Canadian Journal of Zoology 72:1831-1836.
  16. Wilson, D. E., and D. M. Reeder (editors). 1993. Mammal species of the world: a taxonomic and geographic reference. Second edition. Smithsonian Institution Press, Washington, DC. xviii + 1206 pp. Available online at: http://www.nmnh.si.edu/msw/.