Ontologia

Lophozonia cunninghamii

(Hook.) Heenan & Smissen

VULR Monde (IUCN)
Pays · région · aire protégée · écorégion · biome

Graphe en cours d’indexation

Calcul du tissu écologique de Lophozonia cunninghamii.

Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).

Liste rouge IUCN

VU · Vulnérablecritères A4bceDécroissante
Évaluation complète
Évaluation
2018 · v3.1
Altitude
01400 m
Profondeur
m
État de la populationExpert
The species is dominant in cool temperate rainforest across Tasmania (Veblen et al. 1996). Within Victoria the subpopulation has been fragmented by a combination of severe natural and anthropogenic events and stands are smaller here. This subpopulation has been subject to historic decline from habitat loss, Myrtle Wilt and fire. Within Victoria, the subpopulation is estimated have declined by 50% over a three generation period (D. Cameron pers. comm. 2017). The subpopulation here is still in decline due to the impact of fire and climate change. These threats also affect individuals in Tasmania and although we do not have decline information available for the Tasmanian population, it is likely to be similar value to that occurring in Victoria.

Globally, it is estimated that Nothofagus cunninghamii will be subject to population decline of between 30 and 50% over three generations (1817-2117) due to a variety of factors.

Menaces identifiées(10 menaces classées CMP-IUCN)

  • 2_1_4
    Scale Unknown/Unrecorded
    Rapid DeclinesUnknownOngoing
  • 2_2_3
    Scale Unknown/Unrecorded
    Rapid DeclinesUnknownOngoing
  • 12_1
    Other threat
    UnknownUnknownOngoing
  • 4_1
    Roads & railroads
    UnknownUnknownOngoing
  • 5_3_3
    Unintentional effects: (subsistence/small scale) [harvest]
    UnknownUnknownOngoing
  • 8_1_2
    Named species
    UnknownUnknownOngoing
  • 8_1_2
    Named species
    UnknownUnknownOngoing
  • 11_2
    Droughts
    Slow, Significant DeclinesUnknownOngoing
  • 11_3
    Temperature extremes
    Slow, Significant DeclinesUnknownOngoing
  • 7_1_1
    Increase in fire frequency/intensity
    Very Rapid DeclinesUnknownOngoing
Description complète des menacesExpert
The greatest historical threat to the species is from the logging of 'mixed forest' on Tasmania. In sites of logging the regeneration of Nothofagus cunninghamii is poor and the regeneration of the species will not be favoured, leading to quick decline.
 
Nothofagus cunninghamii
experiences severe loss from fire which is the greatest threat to Nothofagus forests in south east Australia and causes large scale declines particularly within Victoria. Rain forests in Tasmania have decreased by 8% from 1950-1996 due to fire. Fire reduces seedling recruitment in both Victoria and Tasmania, reducing species regeneration. Tasmanian subpopulation may be more adversely impacted by this in the future due to their dependence on seed germination for regeneration. The threat of fire is increased by anthropogenic fire regimes and also global climate change.

Nothofagus cunninghamii is also susceptible to fatal infection by Myrtle Wilt (Chalara australis) (spread of the disease may be assisted through the actions of the Pin Hole Borer (Platypus subgranosus) (Veblen et al. 1996, DSE 2005). The risk is greatest to mature trees and is the major cause of gaps in forest cover in Tasmania (Ridley et al. 2000). Victorian subpopulations are considered more susceptible to infection that Tasmanian subpopulations, the cause of this is not yet fully understood. The risk of infection increases with disturbance of canopy cover which can occur as a result of human activity such as logging and road construction (Veblen et al. 1996, Ridley et al. 2000).

Trees are no longer commercially harvested in Victoria and yields are considered sustainable in Tasmania, but the species may be harvested on private property but this is not a major threat. Global climate change, specifically climate drying within the region, is predicted to cause future population decline as these processes reduce recruitment potential. The species is further threatened by clearance of cool temperate rain forest for silviculture and agriculture (D. Cameron pers. comm. 2017).

Habitats préférentiels (classification IUCN)

  • 1_4Forest - Temperate
Mesures de conservation recommandéesExpert
Nothofagus cunninghamii is found in 29 ex situ collections (BGCI 2017). Victorian populations are mainly found in reserves and protected areas; only small pockets occur outside of these. Some forests are also protected in Tasmania (Veblen et al. 1996). The species is a character species for cool- temperate rain forest in Victoria which is listed as 'threatened' under the 'Flora and Fauna Guarantee act 1988'. Within Victoria the species has been assessed as Endangered A4abce, B2ab(ii,iii,v) (Veblen et al. 1996).
Stress écologiques (18)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_3_7Reduced reproductive success
  • 2_3_7Reduced reproductive success
  • 2_3_7Reduced reproductive success
Usage & commerce (2)Expert
  • 11Other household goods
    internationalnational
  • 9Construction or structural materials
    internationalnational
Niche IUCN globaleExpert

Royaumes biogéographiques

Australasian

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Shrub - largeShrub - smallTree - largeTree - small
Références bibliographiques (9)Expert
  1. IUCN. 2018. The IUCN Red List of Threatened Species. Version 2018-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 15 November 2018).
  2. AVH. 2017. Australias Virtual Herbarium: Council of Heads of Australian Herbaria. Canberra Available at: <a href="http://avh.chah.org.au.">http://avh.chah.org.au.</a>.
  3. BGCI. 2017. PlantSearch. Botanic Gardens Conservation International, London. Available at: <a href="https://www.bgci.org/plant_search.php">https://www.bgci.org/plant_search.php</a>.
  4. DPIPWE, Tasmanian Government. 2017. Nothofagus cunninghamii. Hobart (Accessed: Feb 2017).
  5. WCSP. 2017. World Checklist of Selected Plant Families. Available at: <a href="http://apps.kew.org/wcsp/">http://apps.kew.org/wcsp/</a>.
  6. Meier, E. 2015. <i>Wood! Identifying and Using Hundred of Woods WorldWide</i>. The Wood Database.
  7. DSE (Department of Sustainability and Environment). 2005. MYRTLE WILT: A disease of Myrtle Beech. Available at: <a href="http://www.soln.org/wp-content/uploads/2009/06/myrtlewiltfactsheet-2005.pdf">http://www.soln.org/wp-content/uploads/2009/06/myrtlewiltfactsheet-2005.pdf</a>. (Accessed: March 2017).
  8. Ridley, G.S., Bain, J., Bulman, L.S., Dick, M.A. and Kay, M.K. 2000. Threats to New Zealand’s indigenous forests from exotic pathogens and pests. Department of Conservation, New Zealand, Wellington.
  9. Veblen, T.T., Hill, R.S. and Read, J. 1996. <i>The Ecology and Biogeography of Nothofagus Forests</i>. Yale University Press.
Évaluateurs & contributeurs (3)Expert
assessor
Baldwin, H., Barstow, M. & Rivers, M.C.
evaluator
Hill, R.
institutions
Botanic Gardens Conservation International

Baldwin, H., Barstow, M. & Rivers, M.C. 2018. Nothofagus cunninghamii. The IUCN Red List of Threatened Species 2018: e.T61917935A61917949. Accessed on 05 May 2026.

Indicateurs écologiques

Niche thermique

GlobTherm — Bennett 2018

Limites thermiques expérimentales (CTmin/CTmax/LT50 selon publication, mesures en chambre climatique). Repères France à titre indicatif uniquement.

-14 °C50 °C
  • Limites physiologiques -8.8? °C
  • T° moy. France 1981-2010 11.0 °C
  • Projection France 2050 13.7 °C

Sources : GlobTherm (Bennett et al. 2018). Repères France : T moy annuelle CHELSA 1981-2010 + projection DRIAS-2020 GWL20 (+2,7 °C). GlobTherm filtré aux groupes pour lesquels la comparaison à la T air a du sens (ectothermes terrestres + plantes) — exclut endothermes et aquatiques où la nature de la mesure (TNZ ou T eau) rend la comparaison non interprétable.

Répartition mondiale (heatmap GBIF)Construction en cours

0 obs · 0 cellules
Construction par partitions temporelles GBIF0%

Source : GBIF — observations agrégées par hexagones 0.2° × 0.2° (~22km). Filtre qualité : précision coordonnée < 10 km. Coloration quantile (q50/70/90/99). Fond carte : OpenFreeMap · © OpenStreetMap.

Distribution mondiale

Calcul de la distribution GBIF· ~10–60 s

Phénologie

Calcul du calendrier d'apparition· ~5–30 s

Consulter sur les bases externes

Observations & statuts

Cartographie

Bibliographie

Note nomenclaturale & synonymesExpert

Note nomenclaturale

TAXREF v18 — INPN/MNHN

Synonymes (2)— redirigent vers cette page

  • Fagus cunninghamiiHook.
  • Nothofagus cunninghamii(Hook.) Oerst.

Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).