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Capricornis crispus
Japanese serow


By Kensuke Mori

Kingdom: Animalia
Phylum: Chordata
Subphylum: Vertebrata
Class: Mammalia
Order: Artiodactyla
Family: Bovidae
Genus: Capricornis
Species: Capricornis crispus

Geographic Range

The distribution of Japanese serows is restricted to the Japanese islands of Honshu, Kyushu, and Shikoku. (Fukuda, 1995; Kubo, et al., 2001)

Biogeographic Regions
palearctic (Native )

Other Geographic Terms
island endemic

Habitat

Japanese serows inhabit forested areas on mountains. (Fukuda, 1995; Kishimoto and Kawamichi, 1996; Kubo, et al., 2001; Ochiai and Susaki, 2002; Ochiai, 1999)

Habitat Regions
temperate ; terrestrial

Terrestrial Biomes
forest ; mountains

Physical Description

Range mass
30 to 45 kg
(66.08 to 99.12 lb)

Average mass
37 kg
(81.50 lb)

Average length
130 cm
(51.18 in)

Japanese serows are similar in appearance to goats. Their horns average 12 to 16 cm in length. Their body length is approximately 130 cm, and their shoulder height is about 65 cm. Adult serows weigh 30-45 kg, and they are not strongly sexually dimorphic. Their pelage is dark brown, but in the northern part of their range the color is lighter. They possess large infraorbital glands that are used in scent marking their territories. This gland can be seen easily. (Fukuda, 1995; Kubo, et al., 2001; Ochiai and Susaki, 2002)

Other Physical Features
endothermic ; homoiothermic; bilateral symmetry

Sexual Dimorphism
sexes alike

Reproduction

Japanese serows usually form monogamous pairs. However, some males mate with two and occasionally three females in the same breeding season. Two field studies at different locations found a similar proportion of polygynous males (20-30%), suggesting that the proportion of animals that mate polygynously is perhaps fixed in the species. Both sexes form territories that they defend against other individuals of the same sex. Usually male territories almost completely overlap those of a female, but sometimes male territories include territories of more than one female. In these cases, those males are polygynous. Mated pairs remain together every year, perhaps because they hold consistent territories. When a mate is displaced from their territory, their mate remains in the same territory and mates with the individual that takes over the territory of the displaced animal.

Mating System
monogamous ; polygynous

Breeding interval
Japanese serows breed once yearly.

Breeding season
Breeding occurs from Septermber to November.

Range number of offspring
1 to 3

Average number of offspring
1.01

Range gestation period
6.67 to 7.67 months

Average weaning age
5 months

Average time to independence
1 years

Range age at sexual or reproductive maturity (female)
2.5 to 3 years

Range age at sexual or reproductive maturity (male)
2.5 to 3 years

Japanese serows rut in September to November. The young are born in May and June, and they remain with their mother for about a year. Young reach sexual maturity at 2.5 to 3 years of age. Although serows become independent as yearlings, they remain in their natal territory. They disperse between 2 to 4 years of age, but females may inherit their mothers' territories. (Kishimoto and Kawamichi, 1996; Kishimoto, 1989; Ochiai and Susaki, 2002)

Key Reproductive Features
iteroparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); viviparous

Most of the parental investment is provided by the mother. Young serows follow their mothers for a year, and remain in the mother’s territory for 2 to 4 years. Lactation continues until November. Males provide no parental care to the young, although they permit young within their territories. (Kishimoto and Kawamichi, 1996; Kishimoto, 1989; Ochiai and Susaki, 2002)

Parental Investment
altricial ; pre-fertilization (Provisioning, Protecting: Female); pre-hatching/birth (Provisioning: Female, Protecting: Female); pre-weaning/fledging (Provisioning: Female, Protecting: Female); pre-independence (Provisioning: Female, Protecting: Female); post-independence association with parents; inherits maternal/paternal territory

Lifespan/Longevity

Range lifespan
Status: wild

20 to 22 years

Typical lifespan
Status: wild

4.8 to 5.5 years

Average lifespan
Status: captivity

10.0 years
[External Source: Max Planck Institute for Demographic Research]

The maximum longevity is 20 to 21 years for males and 21 to 22 years for females. Life expectancies at birth are 5.3 to 5.5 years for males and 4.8 and 5.1 years for females. One study found that serows live in same territory for 11.7 to 12.4 years. Because serows disperse from their natal territories at 2 to 4 years of age to establish their own territories, they live most of their lives in the territory they established. Also, it is likely that successful establishment of a territory increases an individual's chances of survival greatly, those without territories have greater risk of mortality. (Ochiai and Susaki, 2002; Tokida and Miura, 1988)

Behavior

Average territory size
105-166 km^2

Japanese serows are known to stand on high look outs for extended periods. This behavior could be for the purpose of detecting predators, but may also be to detect territorial rivals. (Fukuda, 1995)

Japanese serows are considered diurnal, but a study using radio collared individual found that they are almost as active during night. (Kishimoto, 1989)

Key Behaviors
terricolous; diurnal ; nocturnal ; sedentary ; solitary ; territorial

Home Range

Japanese serows are solitary animals and form intrasexual territories. They mark their territories with the scent gland located in front of the eyes. Encounter between adults serows of same sex results in aggression, where the intruding serows are chased out of the territories. Deaths from combat injury occur at least among males in some cases. Territory size is affected by the food availability. (Kubo, et al., 2001; Ochiai and Susaki, 2002; Tokida and Miura, 1988)

Communication and Perception

Japanese serows use scent marking to hold territories. Because they are solitary animals and have little occasion to encounter other individuals of the same species, they use scent marking as their primary method of communication. Females use sound to call their young. (Kishimoto, 1989; Fukuda, 1995; Kishimoto, 1989; Kubo, et al., 2001)

Communication Channels
visual ; acoustic ; chemical

Other Communication Modes
scent marks

Perception Channels
visual ; acoustic

Food Habits

Japanese serows are browsers that feed primarily on the buds and leaves of deciduous broad-leaved trees. They also feed on leaves of evergreen coniferous trees and fallen acorns. They sometimes eat flowers and fruits. (Fukuda, 1995; Kubo, et al., 2001; Ochiai, 1999; Takatsuki, et al., 1988)

Primary Diet
herbivore (Folivore )

Plant Foods
leaves; wood, bark, or stems; seeds, grains, and nuts; fruit; flowers

Predation

Known Predators


Japanese serows have no or very few predators other than humans. A potential predator is Ursus thibetanus, Asiatic black bears. However, Asiatic black bears are not highly predatory. Historically, wolves probably preyed on serows, but wolves were exterminated from the serow's range by the early 1900s. More significantly, humans hunted them for meat and hide in the past. They are currently protected as a Japanese natural heritage and hunting is prohibited. Recently, dog predation was found to be a leading source of mortality in some areas. (Kubo, et al., 2001; Ochiai and Susaki, 2002; Tokida and Miura, 1988)

Ecosystem Roles

Because Japanese serows are territorial and their density in any particular area is limited, their impact on vegetation is relatively low. However, some species of plants are affected by their browsing and consequently they have some influence over the vegetation. (Ochiai, 1999)

Economic Importance for Humans: Positive

Traditionally Japanese serows were an important source of meat and hide for people. Currently they are recognized as unique species endemic to Japan and classified as a natural heritage. (Kubo, et al., 2001)

Positive Impacts
food ; body parts are source of valuable material; ecotourism ; research and education

Economic Importance for Humans: Negative

Because they browse on trees, Japanese serows sometimes become pests to the forestry industry as they damage planted trees. They are sometimes killed as a management practice to control damage to forestry plantations. (Kubo, et al., 2001)

Negative Impacts
crop pest

Conservation Status

IUCN Red List of Threatened Species [Link]
Least Concern
More Information

US Federal List [Link]
No special status

CITES [Link]
No special status

Japanese serows were hunted to near extinction by people in the past. They are currently protected as a natural heritage and hunting has been prohibited. They are listed as Lower Risk in IUCN. (Kubo, et al., 2001; Ochiai and Susaki, 2002)

Other Comments

Japanese serows are currently recognized as Capricornis crispus, they were previously recognized under the name Naemorhedus crispus. (Fukuda, 1995; Kishimoto and Kawamichi, 1996; Kubo, et al., 2001; Ochiai and Susaki, 2002; Ochiai, 1999)

For More Information

Find Capricornis crispus information at

Contributors

Tanya Dewey (editor), Animal Diversity Web, University of Michigan Museum of Zoology.

Kensuke Mori (author), University of Michigan, Phil Myers (editor, instructor), Museum of Zoology, University of Michigan.

References

Fukuda, G. 1995. Illustrated pocket book of animals in colour. 5-12, 1 Chome, Akasaka, Minato-ku, Tokyo, Japan: Hokuryukan.

Kishimoto, R. 1989. Early Mother and Kid Behavior of a Typical "Follower", Japanese Serow Capricornis crispus . Mammalia, 53(2): 165-176.

Kishimoto, R., T. Kawamichi. 1996. Territoriality and monogamous pairs in a solitary ungulate, the Japanese serow, Capricornis crispus . Animal Behavior, 52: 673-682.

Kubo, K., Y. Nakagawa, N. Maeda, K. Numata, T. Yamada. 2001. Yama-kei pocket guide 24, Nihon yasei doubutsu. 1-1-33, Shiba-daimon, Minatoku, Tokyo, Japan: YAMA-KEI Publishers Co.,Ltd..

Miura, S., I. Kita, M. Sugimura. 1987. Horn Growth and Reproductive History in Female Japanese Serow. Journal of Mammalogy, Vol.68, No.4.: 826-836.

Miura, S., N. Maruyama. 1986. Winter weight loss in Japanese serow. Journal of Wildlife Management, 50(2): 336-338.

Ochiai, K. 1999. Diet of the Japanese serow (Capricornis crispus) on the Shimokita Peninsula, northern Japan, in reference to variations with a 16-year interval. Mammal study, 24: 91-102.

Ochiai, K., S. Nakama, S. Hanawa, T. Amagasa. 1993. Population dynamics of Japanese serow in relation to social organization and habitat conditions. I. Stability of Japanese serow density in stable habitat conditions. Ecological Research, 8: 11-18.

Ochiai, K., S. Nakama, S. Hanawa, T. Amagasa. 1993. Population dynamics of Japanese serow in relation to social organization and habitat conditions. II. Effects of clear-cutting and planted tree growth on Japanese serow populations. Ecological Research, 8: 19-25.

Ochiai, K., K. Susaki. 2002. Effects of territoriality on population density in the Japanese serow, (Capricornis crispus). Journal of Mammalogy, 83(4): 964-972.

Takatsuki, S., N. Ôsugi, T. Itô. 1988. A Note on the Food Habits of the Japanese Serow at the Western Foothill of Mt. Zao, northern Japan. Journal of the Mammalogical Society of Japan, 13(2): 139-142.

Tokida, K., S. Miura. 1988. Mortality and Life Table of a Japanese Serow (Capricornis crispus) Population in Iwate Prefecture, Japan. Journal of the Mammalogical Society of Japan, 13(2): 119-126.

To cite this page: Mori, K. 2006. "Capricornis crispus" (On-line), Animal Diversity Web. Accessed June 01, 2012 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Capricornis_crispus.html

Disclaimer: The Animal Diversity Web is an educational resource written largely by and for college students. ADW doesn't cover all species in the world, nor does it include all the latest scientific information about organisms we describe. Though we edit our accounts for accuracy, we cannot guarantee all information in those accounts. While ADW staff and contributors provide references to books and websites that we believe are reputable, we cannot necessarily endorse the contents of references beyond our control.

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