Desmocladus glomeratus
K.W.Dixon & Meney
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Desmocladus glomeratus.
Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).
Liste rouge IUCN
VU · Vulnérablecritères D2?Inconnue- Évaluation
- 2016 · v3.1
- Altitude
- 150 – 150 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
No detailed population information available but this rush has been described as abundant or locally frequent on herbarium specimens. At one locality it was reported on a herbarium specimen that male plants were more common than female plants.
Menaces identifiées(5 menaces classées CMP-IUCN)
11_2DroughtsUnknownWhole (>90%)Ongoing1_1Housing & urban areasUnknownUnknownUnknown2_1_3Agro-industry farmingUnknownUnknownOngoing2_3_3Agro-industry grazing, ranching or farmingUnknownUnknownOngoing7_1_1Increase in fire frequency/intensityUnknownUnknownUnknown
Description complète des menacesTexte détaillé évaluation IUCNExpert
This species is found in the Southwest Australia biodiversity hotspot, where one of the main threats has been clearance of native vegetation for agriculture (Conservation International 2015). In the Moresby Range area less than 10% of the original vegetation remains due to historic clearance for agriculture (WAPC 2009). Patches of native vegetation remain throughout the area including near the Howatharra road where this species can be found (WAPC 2009). Outside of protected areas this species is mainly restricted to sites unsuitable for intensive agriculture due to poor low nutrient soils or unsuitable topography like ridges (B. Briggs pers. comm. 2016).
The Moresby Range has historically been used for farmland but there has been an increase in new housing developments and additional infrastructure including roads and water pipelines (WAPC 2009). A new industrial estate is planned at Oakajee not far from the Oakajee nature reserve (WAPC 2009) which could increase the human population in this area. The three locations for this species along the Nanson-Howatherra road are on private property and in 2010 planning permission was submitted by several land owners in this area to change the use of the land from farming to rural small holdings (GHD 2010). This could potentially allow new housing and associated infrastructure to be built in this area.
Fires occur naturally in southwest Western Australia and the flora shows a range of plant adaptations in response to fire, for example reseeding from the soil seed bank (Lambers 2014). This species is reported to be killed by mild fires but new plants germinate from seed (Meney and Pate 1999). In some species of Restionaceae fires can stimulate germination of seeds from the soil seed bank (Lambers 2014). For reseeders like this species too frequent fires can kill adult plants before they have reached maturity but long intervals between fires can cause a decline in the viability of the soil seed bank (Lambers 2014). Therefore appropriate fire management and monitoring of this species habitat is important. In the future this species is suspected to be vulnerable to climate change. In Western Australia they have been changes to rainfall patterns over the last 40 years leading to drier conditions (Climate Commission 2013) and this species sandy shrubland habitat on shallow soils is suspected to be susceptible to droughts (B.Briggs pers. comm. 2016). With projected drier and hotter conditions there may be changes to fire regimes with larger and more intense fires (Climate Commission 2013).
The Moresby Range has historically been used for farmland but there has been an increase in new housing developments and additional infrastructure including roads and water pipelines (WAPC 2009). A new industrial estate is planned at Oakajee not far from the Oakajee nature reserve (WAPC 2009) which could increase the human population in this area. The three locations for this species along the Nanson-Howatherra road are on private property and in 2010 planning permission was submitted by several land owners in this area to change the use of the land from farming to rural small holdings (GHD 2010). This could potentially allow new housing and associated infrastructure to be built in this area.
Fires occur naturally in southwest Western Australia and the flora shows a range of plant adaptations in response to fire, for example reseeding from the soil seed bank (Lambers 2014). This species is reported to be killed by mild fires but new plants germinate from seed (Meney and Pate 1999). In some species of Restionaceae fires can stimulate germination of seeds from the soil seed bank (Lambers 2014). For reseeders like this species too frequent fires can kill adult plants before they have reached maturity but long intervals between fires can cause a decline in the viability of the soil seed bank (Lambers 2014). Therefore appropriate fire management and monitoring of this species habitat is important. In the future this species is suspected to be vulnerable to climate change. In Western Australia they have been changes to rainfall patterns over the last 40 years leading to drier conditions (Climate Commission 2013) and this species sandy shrubland habitat on shallow soils is suspected to be susceptible to droughts (B.Briggs pers. comm. 2016). With projected drier and hotter conditions there may be changes to fire regimes with larger and more intense fires (Climate Commission 2013).
Habitats préférentiels (classification IUCN)
3_8Shrubland - Mediterranean-type Shrubby Vegetation★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This rush is found within two nature reserves, Howatharra and Oakajee, both part of the Moresby Range. The Moresby Range has an active management strategy (WAPC 2009) which identified areas of remnant natural vegetation in the region for further study as potential areas for future conservation management. When the species was first described (Meney et al. 1996) it was cited as being "in urgent need of further surveys to determine the extent of it's distribution and conservation status". The authors recommended the species be considered as rare and endangered (Meney et al. 1996) and the species was also described as having a rare conservation status in 1999 (Meney and Pate 1999). It is listed in Western Australia (Jones 2015) as a Priority 2 conservation species (a poorly known species only known from generally five or less locations and in urgent need of further surveys). There are no known ex situ collections and ex situ conservation is recommended. Further surveys to study population size and the extent of the species distribution are recommended, particularly as the area is infrequently visited by botanists (B. Briggs pers. comm. 2016).
Actions de conservation (3)Conservation Actions Classification Scheme — IUCNExpert
3_4_1Captive breeding/artificial propagation3_4_2Genome resource bank4_3Awareness & communications
Stress écologiques (10)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_3_7Reduced reproductive success2_3_7Reduced reproductive success
Priorités de recherche (5)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_5Threats3_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
Graminoid
Références bibliographiques (11)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2016. The IUCN Red List of Threatened Species. Version 2016-3. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 07 December 2016).
- Conservation International. 2015. Biodiversity Hotspots: Southwest Australia. Available at: <a href="http://www.cepf.net/resources/hotspots/Asia-Pacific/Pages/Southwest-Australia.aspx">http://www.cepf.net/resources/hotspots/Asia-Pacific/Pages/Southwest-Australia.aspx</a>. (Accessed: 10 December 2015).
- Jones, A. 2015. Threatened and Priority Flora List, 11 November 2015. Department of Parks and Wildlife, Western Australia, Kensington.
- Lambers, H. 2014. <i>Plant life in the sandplains in Southwest Australia, a global biodiversity hotspot</i>. University of Western Australia, Crawley.
- Climate Commission. 2013. The Critical Decade: Western Australia climate change impacts. Canberra.
- Bachman, S., Moat, J., Hill, A.W., de la Torre, J. and Scott, B. 2011. Supporting Red List threat assessments with GeoCAT: geospatial conservation assessment tool. In: V. Smith and L. Penev (eds) e-Infrastructures for data publishing in biodiversity science. <i>Zookeys</i> 150: 117–126.
- GHD Environmental Consultancy. 2010. Shire of Chapman Valley, Local planning scheme No. 2. Environmental Review.
- WAPC - Western Australia Planning Commission. 2009. Moresby Range Management Strategy. Western Australia Planning Commission , Perth.
- Olson, D.M., Dinerstein, E., Wikramanayake, E.D., Burgess, N.D., Powell, G.V.N., Underwood, E.C., D'Amico, J.A., Itoua, I., Strand, H.E., Morrison, J.C., Loucks, C.J., Allnutt, T.F., Ricketts, T.H., Kura, Y., Lamoreux, J.F., Wettengel, W.W., Hedao, P. and Kassem, K.R. 2001. Terrestrial ecoregions of the world: a new map of life on earth. <i>Bioscience</i> 51: 933-938.
- Meney, K.A. and Pate, J.S. 1999. <i>Australian Rushes</i>. University of Western Australia Press, Nedlands.
- Meney, K.A., Pate, J.S. and Dixon, K.W. 1996. New species of Restionaceae from Western Australia. <i>Telopea</i> 6(4): 649-666.
Évaluateurs & contributeurs (4)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Williams, E.
contributor
Budden, A.
evaluator
Briggs, B.
facilitators
Hargreaves, S.
Williams, E. 2016. Desmocladus glomeratus. The IUCN Red List of Threatened Species 2016: e.T22486232A22488458. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s