Calochilus cupreus
R.S.Rogers
Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
CR · En danger critiquecritères B1ab(i,ii,iii,iv,v)+2ab(i,ii,iii,iv,v); C2a(ii)↘Décroissante- Évaluation
- 2022 · v3.1
- Altitude
- – m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
It is estimated that over 90% of the species' suitable habitat has been cleared within the species' former distribution in the past 100 years. The Copper Beard-orchid was described as locally common near McLaren Vale in 1918 (Bates 2011). However, despite active searching, the species has not been relocated at this location and the McLaren Vale subpopulations are now considered extinct due to clearing of habitat for agriculture (Bates 2007, DENR 2009). Therefore, at least two subpopulations at McLaren Vale have been lost within the last 90 years. Hence the species' total population trend is decreasing and this decline continues to occur in the last remaining subpopulation of the species in Aldinga Scrub Conservation Park, in the absence of clearing for agriculture. In 2012 and 2013, only 34 plants emerged and flowered in Aldinga Scrub Conservation Park (J. Quarmby pers. comm. 2014). In 2014, following the species’ habitat being damaged by a fire truck attending to a small bushfire that occurred in the park, only 13 flowering plants were recorded; and in 2015 only one flowering plant was identified (NOSSA 2016). However, there are insufficient data to indicate if the decline occurred within an appropriate three generation period (estimated to be 45 years) and whether the population size reduction was substantial, severe or very severe. While the number of flowering plants recorded in surveys has declined, the total population size is likely to remain between 90–100 mature individuals.
Menaces identifiées(14 menaces classées CMP-IUCN)
8_2_2Named speciesUnknownUnknownFuture9_3_1Nutrient loadsUnknownUnknownOngoing1_1Housing & urban areasPast, Unlikely to Return2_1_3Agro-industry farmingPast, Unlikely to Return2_3_3Agro-industry grazing, ranching or farmingPast, Unlikely to Return5_2_1Intentional use (species is the target)Ongoing6_1Recreational activitiesOngoing7_1_1Increase in fire frequency/intensityOngoing8_1_1Unspecified speciesOngoing8_1_2Named speciesOngoing
+ 4 menaces supplémentaires
Description complète des menacesTexte détaillé évaluation IUCNExpert
Past threats to the Copper Beard-orchid were the removal of suitable habitat through native vegetation clearance for agriculture and habitat degradation by livestock grazing. The last remaining area of occupied suitable habitat occurs in Aldinga Scrub Conservation Park. This reserve is small and entirely surrounded by residential and agricultural land (Wollaston 1989).
The greatest threat to the species is considered to be weed invasion and site disturbance from recreational activities (Willson and Bignall 2008). The species is threatened by degradation of habitat through invasion by environmental weeds (DENR 2009) including Perennial Veld Grass (Ehrharta calycina), Bridal Creeper (Asparagus asparagoides), Soursob (Oxalis pes-caprae), and European Olive (Olea europaea). Perennial Veld grass has become increasingly dominant throughout Aldinga Scrub Conservation Park (Kraehenbuehl, 1989) and is the most significant weed problem in the reserve (DEP 1992). Trampling from foot traffic, illegal horse and bike riding, and occasional vehicle use occur in the park (DEP 1992).
Other threats identified for the Copper Beard-orchid include inappropriate fire regimes (Willson and Bignall 2008, DENR 2009), illegal collection and grazing by European Rabbits (Oryctolagus cuniculus) (Willson and Bignall, 2008).
Potential threats include fertiliser spray drift from agricultural land and erosion (DEP 1992). The species occurs within 2 km of confirmed or suspected Phytophthora infestations (Willson and Bignall 2008).
The greatest threat to the species is considered to be weed invasion and site disturbance from recreational activities (Willson and Bignall 2008). The species is threatened by degradation of habitat through invasion by environmental weeds (DENR 2009) including Perennial Veld Grass (Ehrharta calycina), Bridal Creeper (Asparagus asparagoides), Soursob (Oxalis pes-caprae), and European Olive (Olea europaea). Perennial Veld grass has become increasingly dominant throughout Aldinga Scrub Conservation Park (Kraehenbuehl, 1989) and is the most significant weed problem in the reserve (DEP 1992). Trampling from foot traffic, illegal horse and bike riding, and occasional vehicle use occur in the park (DEP 1992).
Other threats identified for the Copper Beard-orchid include inappropriate fire regimes (Willson and Bignall 2008, DENR 2009), illegal collection and grazing by European Rabbits (Oryctolagus cuniculus) (Willson and Bignall, 2008).
Potential threats include fertiliser spray drift from agricultural land and erosion (DEP 1992). The species occurs within 2 km of confirmed or suspected Phytophthora infestations (Willson and Bignall 2008).
Habitats préférentiels (classification IUCN)
3_8Shrubland - Mediterranean-type Shrubby Vegetation
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species is listed as Critically Endangered under the Australian Government Environment Protection and Biodiversity Conservation Act 1999.
Recovery Plan:
There should not be a recovery plan for the Copper Beard-orchid as the approved Conservation Advice for the species provides sufficient direction to implement priority actions, mitigate against key threats and enable recovery.
Primary Conservation Actions Needed:
Conservation and Management Actions:
Invasive species
Habitat loss disturbance and modifications
Fire
Disease
Stakeholder Management
Research Needed:
Survey and Monitoring priorities
Information and research priorities
Recovery Plan:
There should not be a recovery plan for the Copper Beard-orchid as the approved Conservation Advice for the species provides sufficient direction to implement priority actions, mitigate against key threats and enable recovery.
Primary Conservation Actions Needed:
- Prevent further habitat disturbance.
- Maintain and enhance existing and potential habitat.
- Enable recovery of additional sites and/or populations.
- Effectively administer the recovery effort.
Conservation and Management Actions:
Invasive species
- Identify and control weeds such as Perennial Veld Grass, Bridal Creeper, Soursob and European Olive in the local area that could become a threat to the Copper Beard-orchid. Consult with local experts in determining the most appropriate control methods for these weeds without having a detrimental effect on the Copper Beard-orchid.
- Restore degraded habitat using bush regeneration techniques.
- Control invasive pests such as rabbits using appropriate methods.
Habitat loss disturbance and modifications
- Where possible, protect the species by ensuring walking trails are away from the species’ habitat (DEP 1992).
- Undertake appropriate seed and mycorrhizal fungi collection and storage to ensure the persistence of the species if there is further habitat loss or disturbance.
- Propagate seed stock at the Adelaide Botanic Garden in view of reintroducing plants into its native habitat. Involve local community groups in any future reintroduction programme.
- Establish a representative ex situ insurance population in the Adelaide Botanic Garden.
Fire
- Implement an appropriate fire management regime for protecting the species’ habitat, ensuring there are no fires during the above ground phase of the species’ life cycle.
- The species is thought to re-sprout after fire. Consequently, it is optimal to have prescribed burns when the species is below ground in summer.
- Provide maps of known occurrences to local and state Rural Fire Services and seek inclusion of mitigation measures in bush fire risk management plan/s, risk register and/or operation maps.
Disease
- Implement suitable hygiene protocols to control the spread of pathogens to protect the species from outbreaks of Phytophthora cinnamomi, by controlling the movement of vehicles, horses and human traffic into the species’ habitat.
Stakeholder Management
- Provide signage in the Aldinga Scrub Conservation Park to encourage the public to keep to established paths; to keep horses out of the park; and to avoid collecting or damaging plant specimens.
- Raise awareness of the problems associated with illegal collection of specimens.
- Prepare and display leaflets for park visitors, SA Department of Environment and Heritage staff and adjoining Councils, landholders and the community to raise awareness of the need to conserve this species.
- Ensure land owners and managers are aware of the vulnerability of the species to herbicide or pesticide spray drift and fertiliser runoff.
- Consult with the Kaurna Nation Indigenous representatives on the significance of this species to Aboriginal people.
Research Needed:
Survey and Monitoring priorities
- More precisely assess population size, distribution, ecological requirements and the relative impacts of threatening processes.
- Undertake survey work in suitable habitat and potential habitat to locate any additional populations.
- Design and implement a monitoring programme or, if appropriate, support and enhance an existing programme.
- Monitor the progress of recovery, including the effectiveness of management actions and the need to adapt them if necessary.
Information and research priorities
- Implement an annual census to monitor emergence and reproductive success for the species.
- Investigate options for enhancing the existing population or establishing additional populations.
- Identify optimal fire regimes for regeneration (vegetative regrowth and/or seed germination), and the species’ response to other prevailing fire regimes.
- Undertake seed germination and mycorrhizal trials to determine the requirements for the successful establishment of insurance populations and translocations.
- Incorporate management actions for the species into the Aldinga Scrub Conservation Park Management Plan.
Actions de conservation (5)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection2_1Site/area management2_2Invasive/problematic species control3_4_1Captive breeding/artificial propagation4_3Awareness & communications
Stress écologiques (23)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_2Species disturbance2_3_2Competition2_3_2Competition2_3_2Competition2_3_2Competition2_3_2Competition2_3_7Reduced reproductive success
Priorités de recherche (4)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology2_2Area-based Management Plan3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Australasian
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Forb or HerbGeophyte
Références bibliographiques (16)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2022. The IUCN Red List of Threatened Species. Version 2022-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 08 December 2022).
- IUCN Standards and Petitions Committee. 2019. Guidelines for Using the IUCN Red List Categories and Criteria. Version 14. Prepared by the Standards and Petitions Subcommittee. Available at: <a href="http://www.iucnredlist.org/documents/RedListGuidelines.pdf">http://www.iucnredlist.org/documents/RedListGuidelines.pdf</a>.
- Department of the Environment. 2016. AOO and EOO of the Copper beard-orchid (<i>Calochilus cupreus</i>). Department of the Environment, Canberra.
- Threatened Species Scientific Committee (TSSC). 2016. Conservation Advice: <i>Calochilus cupreus</i> copper beard-orchid. Department of the Environment, Canberra. Available at: <a href="http://www.environment.gov.au/biodiversity/threatened/species/pubs/46998-conservation-advice-05052016.pdf">http://www.environment.gov.au/biodiversity/threatened/species/pubs/46998-conservation-advice-05052016.pdf</a>.
- State Herbarium of South Australia. 2014. <i>Adelaide Herbarium database (ADHERB)</i>. Records extracted March 2014.
- Bates, R.J. 2011. <i>South Australia’s Native Orchids</i>. Native Orchid Society of South Australia, Adelaide.
- Newman, B.J. 2009. Orchids as indicators of ecosystem health in urban bushland fragments. PhD Thesis, Murdoch University, Perth, Western Australia.
- Department for Environment and Natural Resources. 2009. Copper beard-orchid (<i>Calochilus cupreus</i>). Threatened Species Profile. Department for Environment and Natural Resources, Adelaide.
- Swarts, N.D. and Dixon, K. 2009. Terrestrial orchid conservation in the age of extinction. <i>Annals of Botany</i> 104: 543–556.
- Willson, A. and Bignall, J. 2008. Draft Regional Recovery Plan for Threatened Species and Ecological Communities of Adelaide and the Mount Lofty Ranges, South Australia. Department for Environment and Heritage, South Australia.
- Bates, R.J. 2007. <i>South Australian Native Orchids (electronic version)</i>. Native Orchid Society of South Australia, Adelaide.
- Bower, C.C. and Branwhite, P. 1993. Observations on the pollination of <i>Calochilus campestris</i>. <i>Orchadian</i> 11: 2.
- Department for Environment and Planning. 1992. Aldinga Scrub Conservation Park Management Plan. Department for Environment and Planning, Adelaide.
- Bates, R.J. and Webber, J.Z. 1990. <i>Orchids of South Australia</i>. South Australian Government Printer, Adelaide.
- Kraehenbuehl, D.N. 1989. Introduced plants. In: E.M. Wollaston (ed.), <i>The Aldinga Scrub Conservation Park: A report on its history and natural values</i>, The Nature Conservation Society of South Australia Inc., Adelaide.
- Wollaston, E.M. (ed.). 1989. <i>The Aldinga Scrub Conservation Park: A report on its history and natural values</i>. The Nature Conservation Society of South Australia Inc., Adelaide.
Évaluateurs & contributeurs (4)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Australian Government, Threatened Species Scientific Committee
contributor
Quarmby, J.
evaluator
Rankou, H. & Zimmer, H.
facilitators
Mastroanni, E., Zimmer, H. & Hilton-Taylor, C.
Australian Government, Threatened Species Scientific Committee 2022. Calochilus cupreus. The IUCN Red List of Threatened Species 2022: e.T206753260A206753270. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.