Calochilus pulchellus
D.L.Jones
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Calochilus pulchellus.
Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).
Liste rouge IUCN
EN · En dangercritères B2ab(iii); D?Inconnue- Évaluation
- 2025 · v3.1
- Altitude
- 20 – 560 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
There are approximately 231 known plants: 180 in NSW and 51 at the single known subpopulation in Victoria (Backhouse pers. comm. 27 May 2021). In 2011, the known population size was approximately 30 individuals from four subpopulations (Stephenson 2011). The increase in the number of subpopulations and plants is attributed to targeted survey effort in the Shoalhaven region (Towle et al. 2020) and the chance discovery of the species in Vic. The targeted surveys in 2019 located 89 individuals at previously unknown locations, from a survey effort of 56 person hours across four days, including 76 km of transects corresponding to ~28.4 ha of transect survey area (Towle et al. 2020). Further targeted surveys in 2020 located an additional 12 individuals at previously unknown locations, from a survey effort of 89 person hours across six days, including 111 km of transects and ~33.7 ha of transect survey area (Ecoplanning 2021). The Pretty Beard-orchid was not detected at four of the six new locations surveyed in 2020 (Ecoplanning 2021).
Menaces identifiées(8 menaces classées CMP-IUCN)
11_3Temperature extremesMajority (50-90%)Ongoing1_1Housing & urban areasMinority (<50%)Past, Likely to Return5_2_4Motivation Unknown/UnrecordedMinority (<50%)Ongoing5_3_4Unintentional effects: (large scale) [harvest]Minority (<50%)Ongoing6_1Recreational activitiesMinority (<50%)Ongoing7_1_1Increase in fire frequency/intensityMajority (50-90%)Future8_1_1Unspecified speciesMajority (50-90%)Ongoing8_1_2Named speciesOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
The main threats to the Pretty Beard-orchid are listed, including threats known to be currently operating, recent historical threats, and projected future threats. The main current threats to the Pretty Beard-orchid include fire regimes that cause declines in biodiversity (inferred), trampling and illegal collection (observed/suspected), grazing by deer (suspected) and climate change (projected). Urban development has been observed to impact the species in 2008, although most known subpopulations are now within national parks or reserves, with the exception of Vincentia (south) where plants occur on private property that is in the process of transferral to national park, one plant (Naval College Rd) on private property that is threatened by development, and 19 plants on private property near Hyam’s Beach. Timber harvesting (suspected) is a potential threat to the species, as the Victorian subpopulation occurs in close proximity to state forest, and potentially suitable habitat exists in areas subject to timber harvesting pressures in eastern Vic and southeast NSW. Climate change (projected) is projected to lead to increased temperatures, changes in rainfall patterns and an increased risk of fire danger weather and extreme events, which in turn may negatively impact flowering and recruitment, growing period and habitat quality. In addition, there are several minor or potential threats to the Pretty Beard-orchid that are not included. Grazing by stock has been observed to impact the only known plant at Naval College Rd (Stephenson 2015). Grazing is likely to have degraded habitat at this site, although the species may still persist underground. However, grazing by stock is unlikely to be a threat to plants at other sites, and is therefore not included. Phytophthora cinnamomi is confirmed to be present at Vincentia (south), but it is unknown what impact (direct or indirect) this pathogen is having on the species (Coutts-McClelland pers. comm. 24 June 2021). Grazing by invertebrates and suspected macropods has been noted at the Vincentia subpopulation (Coutts-McClelland pers. comm. 21 February 2022), and is likely to occur at other sites. However, it is unclear whether rates of herbivory are high, and further research is needed to determine whether herbivory from invertebrates and macropods is likely to pose a threat to the species. Lack of pollination is a threat for many orchids with specialised pollinator interactions, including species that sexually attract male insects (Reiter et al. 2017, Phillips et al. 2020). However, most Calochilus species self-pollinate if they aren’t pollinated by insects within the first few days, and the Pretty Beard-orchid has been observed to have a high rate of natural fruit set (Coutts-McClelland pers. comm. 21 February 2022), suggesting that the Pretty Beard-orchid is likely to be able to set seed in the absence of pollinators.
Habitats préférentiels (classification IUCN)
1_4Forest - Temperate★3_4Shrubland - Temperate★5_3Wetlands (inland) - Shrub Dominated Wetlands★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Conservation and management priorities
Habitat loss disturbance and modifications
Habitat loss disturbance and modifications
- Complete the transfer of the Vincentia (south) site into Jervis Bay National Park and investigate the possibility of inclusion of other unprotected habitat into the public conservation estate.
- Ensure locations of subpopulations are kept updated on state databases, in particular those used by fire and land management agencies. Ensure the precise location of subpopulations is not publicly available.
- Avoid undertaking planned burns of the species or its habitat during the species’ growing season (mid-autumn to early summer) and ensure habitat quality is not compromised as a result of any burn including appropriate post-fire monitoring and weed and herbivore control.
- Prevent trampling at Little Forest Plateau and recreational access to Vincentia (south) by installing access barriers or fences, where appropriate.
- Determine potential habitat for the species in the NSW and Vic forestry estate. Undertake pre-harvest surveys for the Pretty Beard-orchid in areas of suitable habitat designated for forestry activity and implement 100 m buffer exclusion zones from any forestry activity around all subpopulations.
- Conduct post-harvest surveys (>3 years after clearing) in areas of potentially suitable habitat in the NSW and Vic forestry estate, particularly along trails, to determine if the species is capable of colonising disturbed areas.
- Encourage the removal of stock from the private property site at Vincentia (Naval College Road). Grazing, although likely to degrade the habitat of the species, may not necessarily kill the orchid, and as such, this subpopulation should still be considered extant even if the orchid is not observed for lengthy periods of time (as the species has been shown to persist without detection for 20 years at Woollamaia Nature Reserve).
- Protect individuals from browsing by feral animals and macropods (including discrete caging of individuals or fencing of habitat) where necessary. Consider caging individuals post-fire if herbivores are likely to be present in the area.
- Control deer populations when there is evidence of their presence.
- Implement Phytophthora cinnamomi management plans to ensure that:
- The pathogen is not spread within the wild population (part of which is already infected) as far as can be avoided (DOEE 2018)
- Mitigation measures (e.g., treatment with phosphite (phosphonate)) are implemented if required and monitored for any signs of phytotoxicity.
- Continue and maintain seed collection and fungal symbionts for ex situ seed banking, with periodic testing of seed viability through germination testing, as per the Plant Germplasm Conservation Guidelines (Martyn Yenson et al. 2021). Consider caging inflorescences prior to seed collection, to ensure they are not impacted by herbivores.
- Develop ex situ propagation methods and, if appropriate, translocations in accordance with the Guidelines for the Translocation of Threatened Plants in Australia (Commander et al. 2018). Propagation of other Calochilus species in ex situ cultivation has proven difficult (Wright et al. 2006) and ex situ propagation methods for this species are currently the subject of a research project by the Australian Botanic Garden Mount Annan.
- Where translocations are used, monitor all translocated individuals to maturity, seed set and recruitment to ensure they are viable and are contributing to a reduction in the extinction risk for the species.
- Map the exposure of the species to climate change using distribution modelling and climate change projections, to locate existing habitat patches and identify future habitat that would be suitable for the species under future climate change scenarios.
- Identify climate refuges suitable for translocation, ensuring some are geographically distant enough to increase the number of the locations of the species (see “Ex situ recovery actions”) if suitable habitat exists elsewhere. Where translocations are used, monitor all translocated individuals to maturity, seed set and recruitment to ensure they are viable and are contributing to a reduction in the extinction risk for the species.
- Undertake vulnerability assessments of the species’ sensitivity and adaptive capacity to changing climate conditions, which draw from genetic, physiological or ecological evidence.
- The Pretty Beard-orchid is currently included in the NSW Saving Our Species Program, which has facilitated increased survey and management actions. Inclusion in such programmes should be supported.
- Engage and involve Traditional Owners in conservation actions, including surveying for new populations and management actions.
- Liaise with the local community and government agencies to ensure that up-to-date population data and scientific knowledge inform the implementation of conservation actions for this species and, where appropriate, orchid conservation groups.
- Engage community groups by encouraging participation in surveys for the species, while limiting public knowledge of known subpopulations.
- Inform landowners and managers of sites where there are known populations and consult with these groups regarding options for conservation management and protection of the species, including the removal of grazing pressures.
- Ensure land management is sympathetic to the long-term requirements of the species and where possible negotiate land management agreements.
- Further surveys are a priority for this species. Conduct targeted surveys throughout the range of the Pretty Beard-orchid to better determine its population size. Surveys could investigate the large area between the known NSW and Vic subpopulations, as well as further surveys near known subpopulations including on private property.
- Determine trends in population size and distribution.
- Determine threats and their impacts; and,
- Monitor the effectiveness of management actions and the need to adapt them if necessary.
- Work with Traditional Owners to divulge any traditional knowledge associated with the species ensuring the practices to record, store and share this knowledge are mutually supported.
- Determine critical habitat for the Pretty Beard-orchid, including key microhabitat features that are important for the long-term survival of the species.
- Identify fire regimes, including fire season, that are detrimental to the species and those that allow population persistence.
- Investigate the impact of projected climate change-related threats (increase in the frequency and severity of fire and drought, increase in temperature and changes in rainfall patterns) on the suitability of habitat for the species.
- Continue investigations into propagation and ex situ propagation and growing methods for the Pretty Beard-orchid.
- Identify the pollinator(s) of the Pretty Beard-orchid and investigate its biology and ecological requirements, including its abundance in the landscape. Confirm that Pretty Beard-orchid flowers are capable of setting seed if pollinators are not present.
- Identify which mycorrhizal partners are required for germination of the Pretty Beard-orchid, including their abundance in the landscape.
Actions de conservation (5)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection2_1Site/area management3_3_1Reintroduction3_4_2Genome resource bank4_3Awareness & communications
Stress écologiques (11)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance2_2Species disturbance
Priorités de recherche (6)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_5Threats1_6Actions3_1Population trends3_4Habitat 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 (30)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2025. The IUCN Red List of Threatened Species. Version 2025-1. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 27 March 2025).
- Bureau of Meteorology. 2022. Recent and historical rainfall maps. Available at: <a href="http://www.bom.gov.au/climate/maps/rainfall">http://www.bom.gov.au/climate/maps/rainfall</a>. (Accessed: 21st February, 2022).
- IUCN (International Union for Conservation of Nature). 2022. Guidelines for Using the IUCN Red List Categories and Criteria. Version 15. Available at: <a href="http://www.iucnredlist.org/documents/RedListGuidelines.pdf">http://www.iucnredlist.org/documents/RedListGuidelines.pdf</a>.
- DELWP. 2021b. Draft Threatened Species Assessment for <i>Calochilus richiae</i>. Department of Environment, Land, Water and Planning, Victoria.
- New South Wales Aboriginal Land Council. 2021. Map of Local Aboriginal Land Council boundaries. Available at: <a href="https://alc.org.au/">https://alc.org.au/</a>. (Accessed: January 5, 2021).
- New South Wales Aboriginal Land Council. 2021. Map of Local Aboriginal Land Council boundaries. Available at: <a href="https://alc.org.au/">https://alc.org.au/</a>. (Accessed: 5th January, 2021).
- Jones, D.L. 2021. <i>A Complete Guide to Native Orchids of Australia. 3rd edition</i>. Reed New Holland, Sydney.
- Martyn Yenson, A.J., Offord, C.A., Meagher, P.F., Auld, T.D., Bush, D., Coates, D.J., Commander, L.E., Guja, L.K., Norton, S.L., Makinson, R.O., Stanley, R., Walsh, N., Wrigley, D. and Broadhurst, L. 2021. <i>Plant Germplasm Conservation in Australia: Strategies and guidelines for developing, managing and utilising ex situ collection. Third edition</i>. Australian Network for Plant Conservation, Canberra.
- Ecoplanning. 2021. Targeted surveys for <i>Calochilus pulchellus</i>. Report prepared for NSW Department of Planning, Industry and Environment. Department of Planning, Industry and Environment.
- PlantNet. 2021. New South Wales Flora Online page for <i>Calochilus pulchellus</i>. Available at: <a href="https://plantnet.rbgsyd.nsw.gov.au/cgi-bin/NSWfl.pl?page=nswfl&lvl=sp&name=Calochilus~pulchellus">https://plantnet.rbgsyd.nsw.gov.au/cgi-bin/NSWfl.pl?page=nswfl&lvl=sp&name=Calochilus~pulchellus</a>. (Accessed: 9th June, 2021).
- Janissen, B., French, G., Selby-Pham, J., Lawrie, A.C. and Huynh, T. 2021. Differences in emergence and flowering in wild, re-introduced and translocated populations of an endangered terrestrial orchid and the influences of climate and orchid mycorrhizal abundance. <i>Australian Journal of Botany</i> 69: 9-20.
- Aboriginal Victoria. 2021. Map of formally recognised Traditional Owners. Available at: <a href="https://achris.vic.gov.au/weave/wca.html">https://achris.vic.gov.au/weave/wca.html</a>. (Accessed: March 30, 2021).
- Kotilínek, M., Těšitelová, T., Košnar, J., Fibich, P., Hemrová, L., Koutecký, P., Münzbergová, Z. and Jersáková, J. 2020. Seed dispersal and realized gene flow of two forest orchids in a fragmented landscape. <i>Plant Biology</i> 22: 522-532.
- Phillips, R.D., Reiter, N. and Peakall, R. 2020. Orchid conservation: from theory to practice. <i>Annals of Botany</i> 126(3): 345-365.
- Shefferson, R.P., Jacquemyn, H., Kull, T. and Hutchings, M.J. 2020. The demography of terrestrial orchids: life history, population dynamics and conservation. <i>Botanical Journal of the Linnean Society</i> 192: 315–332.
- Towle, B., Coutts-McClelland, K. and Deards, S. 2020. Searching for Pretty Beards: A descriptive ecological model and targeted surveys for the rare <i>Calochilus pulchellus</i> (Orchidaceae). <i>Cunninghamia </i> 20: 193-198.
- Jasinge, N.U., Huynh, T. and Lawre, A.C. 2018b. Changes in orchid populations and endophytic fungi with rainfall and prescribed burning in <i>Pterostylis revoluta</i> in Victoria, Australia. <i>Annals of Botany</i> 121: 321–334.
- Jasinge, N.U., Huynh, T. and Lawrie, A.C. 2018a. Consequences of season of prescribed burning on two spring-flowering terrestrial orchids and their endophytic fungi. <i>Australian Journal of Botany</i> 66: 298–312.
- Commander, L.E., Coates, D., Broadhurst, L., Offord, C.A., Makinson, R.O. and Matthes, M. 2018. <i>Guidelines for the Translocation of Threatened Plants in Australia</i>. Australian Network for Plant Conservation, Canberra.
- DOEE. 2018. Threat abatement plan for disease in natural ecosystems caused by <i>Phytophthora cinnamomi</i>. Canberra. Available at: <a href="http://www.environment.gov.au/biodiversity/threatened/publications/threat-abatement-plan-disease-natural-ecosystems-caused-phytophthora-cinnamomi-2018">http://www.environment.gov.au/biodiversity/threatened/publications/threat-abatement-plan-disease-natural-ecosystems-caused-phytophthora-cinnamomi-2018</a>.
- Reiter, N., Vlcek, K., O’Brien, N., Gibson, M., Pitts, D., Brown, G.R., Bower, C.C. and Phillips, R.D. 2017. Pollinator rarity limits reintroduction sites in an endangered sexually deceptive orchid (<i>Caladenia hastata</i>): implications for plants with specialized pollination systems. <i>Botanical Journal of the Linnean Society</i> 184: 122-136.
- Stephenson, A. 2015. Nomination of <i>Calochilus pulchellus</i> for listing under the EPBC Act. Australian Orchid Council.
- Stephenson, A. 2011. <i>Orchid Species of the Shoalhaven, New South Wales, Australia</i>. Nowra.
- New South Wales Threatened Species Scientific Committee. 2008. <i>Calochilus pulchellus</i> – endangered species listing final determination. Available at: <a href="https://www.environment.nsw.gov.au/Topics/Animals-and-plants/Threatened-species/NSW-Threatened-Species-Scientific-Committee/Determinations/Final-determinations/2008-2010/Calochilus-pulchellus-endangered-species-listing">https://www.environment.nsw.gov.au/Topics/Animals-and-plants/Threatened-species/NSW-Threatened-Species-Scientific-Committee/Determinations/Final-determinations/2008-2010/Calochilus-pulchellus-endangered-species-listing</a>.
- New South Wales Threatened Species Scientific Committee. 2008. <i>Calochilus pulchellus</i> – endangered species listing final determination. Available at: <a href="https://www.environment.nsw.gov.au/Topics/Animals-and-plants/Threatened-species/NSW-Threatened-Species-Scientific-Committee/Determinations/Final-determinations/2008-2010/Calochilus-pulchellus-endangered-species-listing">https://www.environment.nsw.gov.au/Topics/Animals-and-plants/Threatened-species/NSW-Threatened-Species-Scientific-Committee/Determinations/Final-determinations/2008-2010/Calochilus-pulchellus-endangered-species-listing</a>.
- Australian National Botanic Gardens. 2007. Aboriginal Plant Use – NSW Southern Tablelands. Available at: <a href="https://www.anbg.gov.au/apu/index.html">https://www.anbg.gov.au/apu/index.html</a>. (Accessed: November 6, 2020).
- Jersáková, J. and Malinová, T. 2007. Spatial aspects of seed dispersal and seedling recruitment in orchids. <i>New Phytologist</i> 176: 237–241.
- Wright, M., Thomson, R., Smith, Z., McQualter, E. and Cross, R. 2006. Royal Botanic Gardens Melbourne contributes to Victorian orchid conservation: <i>ex situ</i> propagation with mycorrhizal fungi. <i>Australasian Plant Conservation: Journal of the Australian Network for Plant Conservation</i> 15: 12-13.
- Jones, D.L. 2006. Miscellaneous new species of Australian Orchidaceae. <i>Australian Orchid Research</i> 5: 68-69.
- Weston, P.H., Perkins, A.J. and Entwhistle, T.J. 2005. More than symbioses: orchid ecology, with examples from the Sydney region. <i>Cunninghamia</i> 9: 1-15.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Australian Government, Threatened Species Scientific Committee
evaluator
Ghalley, B.B. & Zimmer, H.
Australian Government, Threatened Species Scientific Committee 2025. Calochilus pulchellus. The IUCN Red List of Threatened Species 2025: e.T254085233A254086331. Accessed on 05 May 2026.
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