Abies koreana 

Scope: Global
Language: English

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Taxonomy [top]

Kingdom Phylum Class Order Family
Plantae Tracheophyta Pinopsida Pinales Pinaceae

Scientific Name: Abies koreana E.H.Wilson
Common Name(s):
English Korean Fir
Taxonomic Source(s): Farjon, A. 2010. A Handbook of the World's Conifers. Koninklijke Brill, Leiden.

Assessment Information [top]

Red List Category & Criteria: Endangered B2ab(ii,iii,v) ver 3.1
Year Published: 2011
Date Assessed: 2010-09-07
Assessor(s): Kim, Y.-S., Chang, C.-S., Kim, C.-S. & Gardner, M.
Reviewer(s): Thomas, P. & Farjon, A.
The Korean Fir (Abies koreana) has an estimated area of occupancy (AOO) of about 12 km²It occurs in four fragmented locations; Mt. Gaya, Mt. Chiri and Mt. Togyu on the mainland and Mt. Halla on the remote Jeju Island. The distances between each location range from 40–250 km and are likely to be too great to allow for effective gene flow. There is clear and documented evidence of a continuing decline in the AOO and quality of habitat due to a number of factors which include the effects of climate change, pathogen attack and on Mt. Halla the invasion of pines and bamboo (Sasa). For these reasons A. koreana has been assessed as Endangered. The conservation status of this species needs to be carefully monitored as if there is a further reduction of the current AOO of 12 km² to 10 km² or below, then it will qualify as Critically Endangered.
Previously published Red List assessments:

Geographic Range [top]

Range Description:Endemic to South Korea where it is found in the Provinces of: Jeju Island (Mt Halla); Joelanum (Deok-yu-san (Mt Togyu (Deojyu)); Joellabak (Mt. Chiri (Jiri); Gyeongsangnam (Mt Gaya). The actual AOO has been calculated to be ca 12 km2 (Kim et al. 2000).
Countries occurrence:
Korea, Republic of
Additional data:
Estimated area of occupancy (AOO) - km2:12Continuing decline in area of occupancy (AOO):Yes
Estimated extent of occurrence (EOO) - km2:
Number of Locations:4Continuing decline in number of locations:No
Lower elevation limit (metres):1000
Upper elevation limit (metres):1900
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:The subpopulation on Mt Halla (Jeju Island) is today a remnant of a once much greater distribution, much of which was destroyed ca 100 years ago.
Current Population Trend:Decreasing
Additional data:
Continuing decline of mature individuals:Yes
Population severely fragmented:Yes
Continuing decline in subpopulations:Unknown

Habitat and Ecology [top]

Habitat and Ecology:Occurs in sub-alpine areas on shallow mountain soils poor in humus content. Its elevational range is between 1,000 m and 1,900 m asl. The climate is cool temperate, with a summer monsoon bringing the annual precipitation above 1,600 mm. Abies koreana grows in pure stands or mixed with Betula ermanii, Taxus cuspidata, Prunus maximowiczii, P. sargentii, Cornus kousa with an understory of Sasa quelpartensis on Cheju Island. On the mainland it is also mixed with Picea jezoensis, Pinus koraiensis, P. densiflora, Taxus cuspidata, Quercus mongolica var. mandshurica, Cornus controversa, Acer spp. Fraxinus sieboldiana, Magnolia sieboldii, Sorbus commixta, and several genera of low shrubs, e.g. Juniperus, Deutzia, Ribes and Rhododendron. The forest is usually open and essentially dominated by conifers, with A. koreana a minor component.

Use and Trade [top]

Use and Trade: The Korean Fir is a small to medium sized tree that grows slowly and together with its rarity these qualities make it unsuitable as a timber tree. Because of its small stature and compact growth it has been widely used as an ornamental tree, particularly for small gardens.

Threats [top]

Major Threat(s): Abies koreana is facing critical population declines (Kim et al. 1998). Regional decline of A. koreana was first recognized in 1980s (Woo 2009). The continuing decline in the AOO is as a result of trees suffering from die-back and eventual death and is likely as a result of climate change. For example, on Mt Togyu the rate of dead trees sampled was 18.18% (Kim and Choo 2000) while on Mt Halla it amounts to 6.44% (Kim et al. 2007). It is thought that the dieback is most probably the results of complex interactions between multiple environmental factors caused by global warming (Woo 2009).  Abies koreana is also in decline due to vigorous competition from the bamboo Sasa quelpaertensis and invading pine trees on Mt Halla (C.-S. Kim pers. obs.). Studies suggest that damage by the fungal pathogen Racodium therryanum may be a significant inhibitory factor for the natural regeneration of A. koreana on Mt Halla (Cho et al. 2005, 2007). Twenty years ago between 30%-40% of the subpopulation in Deok-yu (10% of the National Park) was destroyed due to the development of a Ski resort.

Conservation Actions [top]

Conservation Actions: It is afforded protection in all its locations, however even with protection 10% of the Togyu (Deok-yu) National Park was destroyed during the development of a ski resort. To reverse the decline of this species and preserve the genetic diversity, it is necessary to increase natural regeneration from seeds; for this to happen there needs to be an understanding of the factors that affect seed germination and initial seedling survival (Cho 2007). More research is needed into the effects of global warming; temperature and water relation seem to be of great significance in Korean Fir dieback, but little is known about this relationship and the direct effects on A. koreana (Woo 2009).

Classifications [top]

1. Forest -> 1.4. Forest - Temperate
suitability:Suitable  major importance:Yes
2. Land/water management -> 2.2. Invasive/problematic species control
2. Land/water management -> 2.3. Habitat & natural process restoration
3. Species management -> 3.4. Ex-situ conservation -> 3.4.1. Captive breeding/artificial propagation
3. Species management -> 3.4. Ex-situ conservation -> 3.4.2. Genome resource bank

In-Place Research, Monitoring and Planning
  Action Recovery plan:Yes
In-Place Land/Water Protection and Management
  Occur in at least one PA:Yes
  Percentage of population protected by PAs (0-100):70
  Invasive species control or prevention:Yes
In-Place Species Management
  Subject to ex-situ conservation:Yes
In-Place Education
  Subject to recent education and awareness programmes:Yes
  Included in international legislation:No
  Subject to any international management/trade controls:No
1. Residential & commercial development -> 1.3. Tourism & recreation areas
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Rapid Declines ⇒ Impact score:Medium Impact: 6 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 2. Species Stresses -> 2.1. Species mortality

11. Climate change & severe weather -> 11.1. Habitat shifting & alteration
♦ timing:Ongoing ♦ scope:Whole (>90%) ♦ severity:Slow, Significant Declines ⇒ Impact score:Medium Impact: 7 
→ Stresses
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation
  • 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.8. Other

1. Research -> 1.2. Population size, distribution & trends
1. Research -> 1.3. Life history & ecology
1. Research -> 1.5. Threats
1. Research -> 1.6. Actions
2. Conservation Planning -> 2.1. Species Action/Recovery Plan
2. Conservation Planning -> 2.2. Area-based Management Plan
3. Monitoring -> 3.1. Population trends
3. Monitoring -> 3.4. Habitat trends

♦  Pets/display animals, horticulture
 International : ✓ 

Bibliography [top]

Cho, H.K., Miyamoto, T., Takahashi, K., Kim, D.S., Hong, S.G. and Kim, J.J. 2005. First report on Racodium therryanum associated with seed infection of Abies koreana in Korea. Journal of Plant Pathology 21(3): 297-300.

Cho, H., Miyamoto, T., Takahashi, K., Hong, S. and Kim, J. 2007. Damage to Abies koreana seeds by soil-borne fungi on Mount Halla, Korea. Canadian Journal of Forest Research 367(2): 371-382.

IUCN. 2011. IUCN Red List of Threatened Species (ver. 2011.2). Available at: http://www.iucnredlist.org. (Accessed: 10 November 2011).

Kim, G.T. and Choo, G.C. 2000. Comparison of growth condition of Abies koreana Wilson by districts. Korean Journal of Environmental Ecology 14: 80-87.

Kim, G.T., Choo, G.C. and Baek, G.J. 1998. Studies on the structure of forest community in subalpine zone of Mt. Halla Abies koreana forest. [In Korean with English summary]. Journal of Korean Forestry Society 87: 366-371.

Kim, G.T., Choo, G.C. and Um, T.W. 1997. Studies on the structure of Abies koreana Community at Subalpine Zone in Hallasan. Korean Journal of Environmental Ecology 21(2): 161-167.

Kim, S.D. and Yoon, W.S. 1991. Regeneration process of Abies koreana forest in Banya, Mt Jiri. Research Reports of Environmental Science Technology Chungnam National University 9: 97-106.

Korea National Arboretum. 2009. Rare Plants Data Book of Korea. Korea National Arboretum.

Lee, C.S. and Cho, H.J. 1993. Structure and dynamics of Abies koreana Wilson community in Mt Gaya. Korean Journal of Ecology 16(1): 75-91.

Lee, Y.W. and Hong, S.C. 1995. Ecological studies on the vegetational characteristics of the Abies koreana forest. Journal of the Korean Forestry Society [In Korean with English summary.] 84: 247-257.

Oh, K.K., Jee,Y. and Park, S.G. 2000. Dynamic patterns of Abies koreana population in Chirisan National Park: central of east area in Chirisan National Park. Korean Journal of Environmental Ecology 13(4): 330-339.

Woo, S.Y. 2009. Forest decline of the world: A linkage with air pollution and global warming. African Journal of Biotechnology 8(25): 7409-7414.

Woo, S.Y., Lim, J.W. and Lee, D.K. 2008. Effects of temperature on photosynthetic rates in Korean Fir (Abies koreana) between healthy and dieback population. Journal of Integrative Plant Biology 50(2): 129-152.

Citation: Kim, Y.-S., Chang, C.-S., Kim, C.-S. & Gardner, M. 2011. Abies koreana. In: . The IUCN Red List of Threatened Species 2011: e.T31244A9618913. . Downloaded on 20 February 2018.
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