This species extends from Japan to Central and Southern China, via Taiwan, Province of China, and Hong Kong to the west, and via the Republic of Korea to the east. Elevation range: 0-2700 m (efloras 2008).
for Arisaema multisectum
Smithsonian Institution, National Museum of Natural History, Department of BotanyVerification Degree:
Card file verified by examination of original publicationPreparation:
Patung., Hupeh, China, Asia-Temperate
Syntype: Engler, H. G. A. 1920. Pflanzenr. 73: 186.
Habitat and Ecology
Habitat and Ecology
This species is a perennial herb found in evergreen and deciduous riparian forest and deforested open sites, located in flood plains along rivers, often near sea level. In Japan it always seems to grow in areas where water deficiency hardly ever occurs and is often found among grasses. Muraoka et al. (1997) found that the most suitable habitat for this species is a forest edge or relatively well illuminated forest understory, where there is little or no water stress. It has been reported from forests, thickets and grasslands in China up to 2700 m a.s.l. (efloras 2008). Systems
In addition to reproduction by seeds, the plants also reproduce vegetatively by cormlets formed around the maternal corm. The plant sheds its leaf in mid-summer and overwinters as corms.
Molecular Biology and Genetics
Barcode data: Arisaema heterophyllum
The following is a representative barcode sequence, the centroid of all available sequences for this species.
Statistics of barcoding coverage: Arisaema heterophyllum
Barcode of Life Data Systems (BOLDS) Stats
Public Records: 2
Specimens with Barcodes: 8
Species With Barcodes: 1
IUCN Red List Assessment
Red List Category Year Assessed
Least Concern Red List Criteria Version
Crook, V. Reviewer/s
Scott, J.A. Contributor/s Justification
is a perennial herb found in central and southern China, Taiwan, Hong Kong, Japan and the Republic of Korea. It has a large estimated extent of occurrence (EOO) of more 2.5 million km2
, This estimate is based on specimen data, some of which is old and some sub-populations may have been lost due to habitat conversion. However, the EOO is still inferred to exceed the threshold for a threatened category. It is often found in riparian forest and more open areas along watercourses and forest clearance, damming, pollution and conversion to rice and fish farming are all threats that are likely to directly affect this species. Its preference for riparian habitats may mean that the area of occupancy (AOO) is in decline due to the habitat changes currently occurring along many of the rivers in the region (although it was not possible to estimate actual values for present and future AOO). The species is considered threatened in Japan, where the majority of rivers have been stripped of their forest habitat (Oshima et al.
1997), and only a few patches remain. However, it is inferred that the area of occupancy (AOO) and population at present exceed the thresholds for a threatened category. In the Rare Plants Data Book of Korea it is listed as nationally Least Concern (Korea national Arboretum 2009). It is found within several protected areas and it is conserved ex situ
in several botanical institutions around the world. It is assessed as Least Concern. Periodic monitoring is recommended to detect any declines as there are ongoing threats to habitat.
There are no population data available for this species. Specimens have been collected consistently over the last 150 years, between 1863 and 2005. Population Trend
Due to forest clearing, the wet conditions required by this species are becoming rare, and in Japan it is considered a threatened species, where it has been listed in the national plant Red-Data Book (Muraoka et al.
1997). Conversion of forest to farmland is occurring throughout the region and this species is likely to have lost a significant extent of suitable habitat over the last few years, particularly in China. An example of this is given by changes within ecoregions where the species is found: for example the Jian Nan subtropical evergreen forests ecoregion, where mos native vegetation has been extirpated. Lowlands have been converted to rice paddy agriculture for centuries and some areas have been more recently converted to plantations of the native conifers Pinus massoniana
and Cunninghamia lanceolata
. Riverine habitats are also under significant threat, with pollution, damming and conversion of flooded areas to rice and fish farming being prevalent threats (Carpenter 2001). In the Changjiang Plain evergreen ecoregion, hundreds of miles of river have been contained between earthen banks and there are severe hydrological and ecological consequences to the Three Gorges Dam Project (Carpenter 2001).
There has been a recent increase in interest for cultivating Arisaema
species (D. Roberts pers. comm. 2008) and it is used as a medicinal plant in China (efloras 2008), and harvesting from the wild may be a threat for this species.
This species is found in several "country parks" in Hong Kong and it is cultivated, with plants growing in several botanical institutions around the world, such as the Botanical Garden in Komaba, Japan; Juniper Level Botanic Garden, Raleigh, US (plants originally from Kaichen Nursery, China); and The Royal Botanic Gardens, Kew, UK (three plants derived from seed from South Korea). The seeds stored in the Millennium Seed Bank, UK, were collected from South Korea. It is also recorded from protected areas such as the Taeanhaean National Park in Korea, the Taroko National Park in Taiwan and the Baishui Jiang Nature reserve in China, although many herbarium records from China fall outside protected areas.
Oshima et al. (1997) concluded that active management of riparian forest in Japan is required to prevent invasion of bamboo into the forests, as this would prevent regeneration of species such as this, species which need the moderate light environment normally found in these forests understories.