Glyptostrobus pensilis

Taxonomy

Assessment Information

Geographic Range

Population

Habitat and Ecology

Threats

Conservation Actions

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Taxonomy [top]

Kingdom	Phylum	Class	Order	Family
PLANTAE	TRACHEOPHYTA	CONIFEROPSIDA	CONIFERALES	CUPRESSACEAE

Scientific Name:

Glyptostrobus pensilis

Species Authority:

(Staunton ex D.Don) K.Koch

Common Name/s:

English

–

Chinese Water Fir

Assessment Information [top]

Red List Category & Criteria:

Critically Endangered C2a(i) ver 3.1

Year Published:

2011

Assessor/s:

Thomas, P., Yang, Y., Farjon, A., Nguyen, D. & Liao, W.

Reviewer/s:

Nguyen, T.H. & Phan, K.L.

Contributor/s:

Justification:

Glyptostrobus pensilis was formerly very widespread in China, Viet Nam and possibly Lao PDR. In China and Viet Nam most of the natural plants have been killed due to expanding agriculture. It appears that there are no plants remaining in the wild in China and that the only remaining natural subpopulations are in Viet Nam and Lao PDR. Although the total number of trees is more than 250, very few, if any are producing viable seed and the majority of trees in Viet Nam are in decline. The species is therefore listed as Critically Endangered under criterion C. It could possibly also meet this under criterion A, but it is not known over what time period the greatest population reduction took place (it could well have been a long slow process exceeding three generations). Given current trends this species could well become Critically Endangered (Possibly Extinct in the Wild) in the near future.

History:

2006	–	Endangered (IUCN 2006)
2006	–	Endangered
2000	–	Data Deficient
1998	–	Data Deficient (Oldfield et al. 1998)
1998	–	Data Deficient
1997	–	Rare (Walter and Gillett 1998)

Geographic Range [top]

Range Description:	This species is found in SE China: Fujian, S Hunan, Guangdong, Guangxi, Jiangxi (it is suggested that most if not all of these supposed occurrences are cultivated plants (Li and Xia 2004, 2005) – there are more than 200,000 mature individuals known in cultivation); introduced on Hainan Island and in Sichuan, possibly natural in SE Yunnan (but this too is disputed). This species is known from nine small localities in Dac Lac province in in Viet Nam (Averyanov 2009). These represent two locations sensu IUCN. Recently several small stands were discovered in Khammouan Province, Lao PDR (Thomas and LePage 2011) - these are considered to represent one location sensu IUCN.
Countries:	Native: China (Fujian - Present - Origin Uncertain, Guangdong - Present - Origin Uncertain, Guangxi - Present - Origin Uncertain, Hainan - Present - Origin Uncertain, Jiangxi - Present - Origin Uncertain, Sichuan - Present - Origin Uncertain, Yunnan - Present - Origin Uncertain); Lao People's Democratic Republic; Viet Nam
Range Map:	Click here to open the map viewer and explore range.

Population [top]

Population:	No wild plants are known to remain in China, although hope remains that a few individuals may still survive. In Viet Nam fewer than 300 trees occur in five localities. Three of these localities have less than 10 trees each. The main stands are located within Earal and Trap Kso nature reserves. No viable seed has been collected from these trees over the last 20 years (Averyanov et al. 2009) In Lao PDR six stands were recently located during surveys of the Nakai plateau. The largest of these was inundated at the completion of the Nam Theun II hydroscheme. The total number of trees remaining is estimated to be less than 100 (Thomas and LePage 2011). Although the total number of trees is more than 250, very few have been known to produce viable seed or to reproduce vegetatively. Within the context of the IUCN definitions, the number of mature individuals is less than 250.
Population Trend:	Decreasing

Population:

No wild plants are known to remain in China, although hope remains that a few individuals may still survive.

In Viet Nam fewer than 300 trees occur in five localities. Three of these localities have less than 10 trees each. The main stands are located within Earal and Trap Kso nature reserves. No viable seed has been collected from these trees over the last 20 years (Averyanov et al. 2009)

In Lao PDR six stands were recently located during surveys of the Nakai plateau. The largest of these was inundated at the completion of the Nam Theun II hydroscheme. The total number of trees remaining is estimated to be less than 100 (Thomas and LePage 2011).

Although the total number of trees is more than 250, very few have been known to produce viable seed or to reproduce vegetatively. Within the context of the IUCN definitions, the number of mature individuals is less than 250.

Population Trend:

Decreasing

Habitat and Ecology [top]

Habitat and Ecology:	A heliophilous species, intolerant of competition and usually growing in pure stands or solitary along streams. In China it is mainly found on river floodplains and in deltas, always near or in water, where it develops a buttressed base and occasionally pneumatophores; also extensively planted along rivers and canals. In Viet Nam and Lao PDR it occurs along streams and in seasonally inundated areas at altitudes between 500 and 700 m asl.
Systems:	Terrestrial

Habitat and Ecology:

A heliophilous species, intolerant of competition and usually growing in pure stands or solitary along streams. In China it is mainly found on river floodplains and in deltas, always near or in water, where it develops a buttressed base and occasionally pneumatophores; also extensively planted along rivers and canals. In Viet Nam and Lao PDR it occurs along streams and in seasonally inundated areas at altitudes between 500 and 700 m asl.

Systems:

Terrestrial

Threats [top]

Major Threat(s):	In China and Viet Nam habitat loss due to intensive agriculture has been the main cause of decline. The subpopulations in Viet Nam are within coffee plantations, the water table has been altered and the trees are no longer producing fertile seed. Illegal logging of live and dead trees within the nature reserves has recently been reported. The largest of the recently discovered stands in Lao PDR were located within the inundation zone of the newly completed Nam Theun II hydroscheme and have been flooded. Several small stands are located outside of this zone on land that has been allocated to villages for forestry or agriculture, and each stand has been impacted to various degrees by logging, construction of fish ponds, and clearing for food crops (Thomas and LePage 2011)

Major Threat(s):

In China and Viet Nam habitat loss due to intensive agriculture has been the main cause of decline. The subpopulations in Viet Nam are within coffee plantations, the water table has been altered and the trees are no longer producing fertile seed. Illegal logging of live and dead trees within the nature reserves has recently been reported.

The largest of the recently discovered stands in Lao PDR were located within the inundation zone of the newly completed Nam Theun II hydroscheme and have been flooded. Several small stands are located outside of this zone on land that has been allocated to villages for forestry or agriculture, and each stand has been impacted to various degrees by logging, construction of fish ponds, and clearing for food crops (Thomas and LePage 2011)

Conservation Actions [top]

Conservation Actions:	Surveys are required of all potential areas of suitable habitat in China to see if any wild plants still remain. The subpopulations in southern Viet Nam and Lao PDR should receive urgent site protection and restoration efforts are required to increase the size and viability of these subpopulations. If that is not done this species could well become Critically Endangered (Possibly Extinct in the Wild).

Conservation Actions:

Surveys are required of all potential areas of suitable habitat in China to see if any wild plants still remain. The subpopulations in southern Viet Nam and Lao PDR should receive urgent site protection and restoration efforts are required to increase the size and viability of these subpopulations. If that is not done this species could well become Critically Endangered (Possibly Extinct in the Wild).

Citation:	Thomas, P., Yang, Y., Farjon, A., Nguyen, D. & Liao, W. 2011. Glyptostrobus pensilis. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.2. <www.iucnredlist.org>. Downloaded on 25 May 2013.
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