Caladenia granitora
Hopper & A.P.Br.
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Calcul du tissu écologique de Caladenia granitora.
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Liste rouge IUCN
EN · En dangercritères B1ab(iii,v)+2ab(iii,v); D↘Décroissante- Évaluation
- 2022 · v3.1
- Altitude
- – m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
As at 5 September 2016 Caladenia granitora is known from four subpopulations comprising a total of 63 mature (flowering) individuals. These include a large population of 50 mature individuals in an area under threat from 4WD recreational activity and a small population of 13 mature individuals in currently undisturbed habitat. Two subpopulations are not known to contain extant mature plants but habitat is intact and it is possible plants were missed given they were found over just a few square metres when seen previously.
- Subpopulation 1. On a granite headland, NE of Cheynes Beach. This is the largest subpopulation, containing 50 mature plants when surveyed in 2015. The primary threat is destruction of habitat by 4WD vehicles. Altered fire regimes may also be a risk to this subpopulation.
- Subpopulation 2. Mount Manypeaks. When surveyed in 1987 this subpopulation contained just 10 mature plants over a few square metres. The area was surveyed again in 2001 by Sarah Barrett and independently by Andrew Brown with no plants located. In 2015 just two leaves that could have been this species were located.
- Subpopulation 3. WSW of Mount Manypeaks. When surveyed in 1987 this subpopulation contained just 8 mature plants over a few square metres. No plants have since been found.
- Subpopulation 4. SW of Cheynes Beach. When surveyed in 2015 this subpopulation contained 13 mature plants.
Caladenia granitora is found in three locations based on the risk of fire occurrence at the four subpopulations. These are regarded as populations by Parks and Wildlife and subpopulations under IUCN. The thynnine wasp pollinator of the species is very territorial and travels just short distances. It is therefore unlikely that pollen transfer will occur between locations. Once pollinated, orchid seed can disperse long distances (Arditti and Ghani 2000), however, most seed falls close to the parent plant (Jersakova and Malinova 2007) and the chances of seed dispersal between locations is likely to be extremely low.
The species has been extensively searched for by competent persons for the past 25 years with few subpopulations/plants found and only one new subpopulation found in recent years (2016). Due to the predictability of its habitat (coastal granites) there is a high likelihood of detection if plants are present. As C. granitora occurs on exposed coastal granites, systematic surveys have targeted these areas during its flowering season (October). The species is easily identified, meaning that volunteers involved with the “Adopt an Orchid Project” and members of The Western Australian Native Orchid Study and Conservation Group have been able to contribute extensively to the survey effort, particularly over the past six years.
All above subpopulations are threatened by altered fire regimes and the genetic and demographic risks associated with small subpopulation size.
Caladenia granitora has a total current population size of 63 mature individuals. This estimate is based on exact counts at each of the two known extant occurrences. Note: no plants were located at Subpopulations 2 and 3 when surveyed in 2015, however, it is possible plants were missed given they were found over just a few square meters when seen previously.
There has been a decline in number of mature individuals at monitored sites since 2013, however this may be attributable to survey or seasonal variation in flowering. Further survey is required to quantify any real decline.
Menaces identifiées(4 menaces classées CMP-IUCN)
12_1Other threatRapid DeclinesWhole (>90%)Future6_1Recreational activitiesRapid DeclinesMajority (50-90%)Ongoing6_3Work & other activitiesRapid DeclinesMajority (50-90%)Future7_1_1Increase in fire frequency/intensitySlow, Significant DeclinesWhole (>90%)Future
Description complète des menacesTexte détaillé évaluation IUCNExpert
Recreational activities
Destruction of habitat by 4WD vehicles and track maintenance is a threat to part of Subpopulation 1. The subpopulation is located within a recreation reserve and adjoins a parking area, road and track. The margins of the parking area and track have been gradually expanding, destroying orchid habitat. Recent works have been carried out on the track, upgrading and resurfacing it to discourage vehicles running off its edge. However, some vehicles are still doing this.
Small population size
As Caladenia granitora is known from just 63 mature individuals, and its habitat is limited to a few coastal granites, the likelihood of the species falling victim to a chance demographic or environmental event is high.
Road maintenance
Threats to the part of Subpopulation 1 alongside a main road include grading, chemical spraying, construction of drainage channels and the slashing of roadside vegetation.
Altered fire regimes
Fire during the summer when plants are dormant has no known detrimental impact on the species. However, fire during late autumn, winter and early spring may adversely affect the viability of populations by directly killing plants and also preventing seed set. Most orchid species emerge from the soil by mid-April and dehisce their seed by late November. The optimum time for fire is therefore between December and mid-April.
Habitats préférentiels (classification IUCN)
3_8Shrubland - Mediterranean-type Shrubby Vegetation★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species is listed as Endangered under the Australian Government Environment Protection and Biodiversity Conservation Act 1999.
In Place
- Monitoring and surveys have been carried out to determine plant numbers and impact of threats.
- Land managers (City of Albany) have been notified of the location and threatened status of Caladenia granitora. Notifications detail their legal obligations in regards to its protection.
- Threatened flora markers have been installed along the main road at Subpopulation 1.
- Seed collected by the Botanic Gardens and Parks Authority (BGPA) from Population 1 is in long term storage.
- Recent works have been carried out on the track running past Subpopulation 1, upgrading and resurfacing it to discourage vehicles running off its edge.
- Included in Western Australian Wildlife Management Program No 20 – Declared Rare and Poorly Known Flora in the Albany District, C.J. Robinson and D.J. Coates 1995. A species recovery plan “Interim Recovery Plan No. 361 Granite Spider Orchid (Caladenia granitora)” has been prepared.
- Caladenia granitora benefits from the preservation of habitat for the threatened bird species, Noisy Scrub-bird, Western Bristlebird and Western Whipbird and two Threatened flora species – Banksia verticillata and Daviesia ovata.
Management Recommendations
- Ongoing monitoring and observations of subpopulation and threats.
- Rehabilitate habitat adjacent to the track through Subpopulation 1.
- Collect and store seeds along with samples of the orchid’s symbiotic fungus to guard against the extinction of natural populations. Collections of seed should aim to sample and preserve the maximum range of genetic diversity possible.
- Develop and implement a translocation proposal if natural populations decline.
- Develop and implement a fire management strategy. Caladenia granitora is thought to be killed by fire if it occurs while the plant is in active growth. It is important therefore that a fire regime with appropriate fire frequency, intensity and seasonality be applied to areas occupied by the species.
- Continue undertaking surveys for new populations.
- Ensure long-term protection of habitat. Parks and Wildlife will investigate ways and means of improving the security of C. granitora habitat at Subpopulation 1. This may include vesting change, acquiring land or developing management plans in consultation with land managers.
- Liaise with land managers and Aboriginal communities to ensure that populations of C. granitora are not accidently damaged or destroyed and its habitat is maintained in suitable condition for the conservation of the species. Aboriginal consultation will take place to determine if there are any issues or interests in areas that are habitat for the species.
- Map habitat critical to the survival of the species to facilitate its protection and appropriate management.
- Promote awareness of the species with general public.
- All known subpopulations of C. granitora need to be maintained to maximise the species’ genetic diversity.
- 4WD access should be excluded from the area of Subpopulation 5 by closing the access track and car park or by fencing the subpopulation.
Actions de conservation (5)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection2_1Site/area management2_3Habitat & natural process restoration3_4_2Genome resource bank4_3Awareness & communications
Stress écologiques (9)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance2_3_7Reduced reproductive success
Priorités de recherche (4)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_5Threats3_1Population trends4Other
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Formes de croissance
Références bibliographiques (17)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).
- Threatened Species Scientific Committee (TSSC). 2018. Conservation Advice <i>Caladenia granitora</i>. Department of the Environment and Energy, Canberra. Available at: <a href="http://www.environment.gov.au/biodiversity/threatened/species/pubs/65292-conservation-advice-11052018.pdf">http://www.environment.gov.au/biodiversity/threatened/species/pubs/65292-conservation-advice-11052018.pdf</a>. (Accessed: 2022).
- Threatened Species Scientific Committee (TSSC). 2018. Conservation Advice <i>Caladenia granitora</>. Department of the Environment and Energy, Canberra. Available at: <a href="http://www.environment.gov.au/biodiversity/threatened/species/pubs/65292-conservation-advice-11052018.pdf">http://www.environment.gov.au/biodiversity/threatened/species/pubs/65292-conservation-advice-11052018.pdf</a>. (Accessed: 2022).
- Brown, A.P., Dixon, K.W., French, C.J. and Brockman, G.B. 2013. <i>Field Guide to the Orchids of Western Australia</i>. Simon Nevill Publications, Fremantle, Western Australia.
- Hoffman, N. and Brown, A.P. 2011. <i>Orchids of Southwest Australia</i>. Published by author, Perth.
- Swarts, N.D., Sinclair, E.A., Francis, A. and Dixon, K.W. 2010. Ecological specialisation in the orchid mycorrhizal interaction leads to rarity in the endangered terrestrial orchid <i>Caladenia huegleii</i>. <i>Molecular Ecology</i> 19: 3226–3242.
- Phillips, R.D., Faast, R., Bower, C.C., Brown, G.R. and Peakall, R. 2009. Implications of pollination by food and sexual deception on pollinator specificity, fruit set, population genetics and conservation of <i>Caladenia</i>. <i>Australian Journal of Botany</i> 57: 287-306.
- Brown, A., Dundas, P., Dixon, K. and Hopper, S. 2008. <i>Orchids of Western Australia</i>. University of Western Australia Press, Crawley, WA.
- Swarts, N.D. 2007. Integrated Conservation of the Rare and Endangered Terrestrial Orchid <i>Caladenia huegelii</i> H.G. Reichb. PhD thesis. The University of Western Australia.
- Jersákova, J. and Malinová, T. 2007. Spatial aspects of seed dispersal and seedling recruitment in orchids. <i>New Phytologist</i> 176: 237-241.
- Hopper, S.D. and Brown, A.P. 2001. Contributions to Western Australian Orchidology: 2. New taxa and circumscriptions in <i>Caladenia</i> (Spider, Fairy and Dragon Orchids of Western Australia). <i>Nuytsia</i> 14: 27-307.
- Batty, A.L. 2001. The role of symbiotic seed germination in the conservation of selected Western Australian terrestrial orchids. PhD thesis. The University of Western Australia.
- Adritti, J. and Ghani, A.K.A. 2000. Numerical and physical properties of orchid seeds and their biological implications. <i>New Phytologist</i> 145: 367-421.
- Western Australian Herbarium. 1998-. FloraBase - the Western Australia Flora. Available at: <a href="https://florabase.dpaw.wa.gov.au/">https://florabase.dpaw.wa.gov.au/</a>. (Accessed: 20 September 2018).
- Robinson, C.J. and Coates, D.J. 1995. Western Australian Wildlife Management Program No 20 – Declared Rare and Poorly Known Flora in the Albany District.
- Ramsay, R.R., Dixon, K.W. and Sivasithamparam, K. 1986. Patterns of infection and endophytes associated with Western Australian orchids. <i>Lindleyana</i> 1: 203-214.
- Stoutamire, W.P. 1983. Wasp-pollinated species of <i>Caladenia</i> (Orchidaceae) in South-western Australia. <i>Australian Journal of Botany </i> 31: 383-394.
Évaluateurs & contributeurs (4)Personnes ayant contribué à l'évaluation IUCNExpert
Australian Government, Threatened Species Scientific Committee 2022. Caladenia granitora. The IUCN Red List of Threatened Species 2022: e.T206711701A206712814. Accessed on 05 May 2026.
Distribution mondiale
Phénologie
Consulter sur les bases externes
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (2)— redirigent vers cette page
- Arachnorchis granitora(Hopper & A.P.Br.) D.L.Jones & M.A.Clem.
- Calonemorchis granitora(Hopper & A.P.Br.) Szlach. & Rutk.
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).