Ontologia

Scleria mackaviensis

Boeckeler

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

Graphe en cours d’indexation

Calcul du tissu écologique de Scleria mackaviensis.

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

Liste rouge IUCN

LC · Préoccupation mineureStable
Évaluation complète
Évaluation
2013 · v3.1
Altitude
01000 m
Profondeur
m
État de la populationExpert
Scleria mackaviensis appears to be locally common along the coast of Queensland and New South Wales. The number of individuals is not known (Fensham and Skull 1999, Hunter 2003).

Menaces identifiées(9 menaces classées CMP-IUCN)

  • 1_3
    Tourism & recreation areas
    Ongoing
  • 2_3_4
    Scale Unknown/Unrecorded
    Ongoing
  • 7_1_3
    Trend Unknown/Unrecorded
    Ongoing
  • 7_2_11
    Dams (size unknown)
    Ongoing
  • 8_1_1
    Unspecified species
    Ongoing
  • 8_1_2
    Named species
    Ongoing
  • 8_1_2
    Named species
    Ongoing
  • 8_1_2
    Named species
    Ongoing
  • 9_1_1
    Sewage
    Ongoing
Description complète des menacesExpert
This species is adapted to a wide range of habitats, many of which are endangered and have been altered for agriculture and pasture. The species most commonly occurs in areas of low human footprint. Threats to plant species in the region include continued clearing, conversion and fragmentation of native vegetation, altered fire regimes, pasture improvement practices, invasive weeds e.g., Parthenum hysterophous, Cinanomum camphora and Lantana camara, overgrazing, construction of dams and irrigation schemes, water pollution and issues with sewage disposal and trampling by tourists. However these may not present direct threats to the species. This species tolerates a wide range of environmental stresses e.g., drought, fire with less than 30% mortality when subject to 100% leaf scorch, strong wind and frost and actually benefits from grazing from macropods or livestock (i.e., grazing increase), being more abundant in constantly grazed areas (Fensham and Skull 1999). The species is often found on disturbed sites such as campsites, schoolgrounds, roadside ditches and tracks and also grows on sites invaded by weeds such as Pteridium esculentum. The spreading rhizome habit allows the taxon to resprout basally after disturbance (Sanderson et al. 2002, McIntyre et al. 2003, Williams 2005, specimen data).

Habitats préférentiels (classification IUCN)

  • 1_4Forest - Temperate
  • 1_5Forest - Subtropical/Tropical Dry
  • 2_1Savanna - Dry
  • 3_4Shrubland - Temperate
  • 3_5Shrubland - Subtropical/Tropical Dry
  • 4_5Grassland - Subtropical/Tropical Dry
Mesures de conservation recommandéesExpert
The taxon does not benefit from any legal protection as it is common in its range. The area where the taxon occurs benefits from some form of protection e.g., Ramsar convention, Conservation Parks, National Parks and Nature Reserves where actions are taken to minimize the impact of the potential threats to the local flora.
Actions de conservation (4)Expert
  • 1_1Site/area protection
  • 1_2Resource & habitat protection
  • 2_1Site/area management
  • 2_3Habitat & natural process restoration
Stress écologiques (12)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
Niche IUCN globaleExpert

Royaumes biogéographiques

Australasian

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

GeophyteGraminoid
Références bibliographiques (12)Expert
  1. IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.1). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 12 June 2013).
  2. Nelder, V.J., Kirkwood, A.B. and Collyier, B.S. 2006. Optimum time for sampling floristic diversity in tropical eucalypt woodlands of northern Queensland. <i>The Rangeland Journal</i> 26(2): 190-2003.
  3. Hunter, J.T. 2005. Floristics an Distribution of Wattle Dry Sclerophyll Forests and Scrubs. <i>Cunningahamia</i> 9(2): 317-323.
  4. McIntyre, S., Heard, K.M. and Martin, T.G. 2003. The Relative Importance of Cattle Grazing in Subtropical Grasslands: Does It Reduce or Enhance Plant Biodiversity? <i>The Journal of Applied Ecology</i> 40(3): 445-457.
  5. Hunter, J.T. 2003. Vegetation and flora of Arakoola Nature Reserve, North Western Slopes, New South Wales. <i>Cunninghamia</i> 8(2): 188-201.
  6. Benson, D. and Howell, J. 2002. Cumberland Plain Woodland ecology then and now: interpretations and implications from the work of Robert Brown and others. <i>Cunninghamia</i> 7(4): 631-650.
  7. Sanderson, E.W., Jaiteh, M., Levy, M.A., Redford, K.H., Wannebo, A.V. and Woolmer, G. 2002. The human footprint and the last of the wild. <i>Bioscience</i> 52(10): 891-904.
  8. Batianoff, G.N., Neldner, V.J. and Sarinda, S. 2000. Vascular plant census and floristic analysis of serpentine landscapes in central Queensland. <i>The Proceedings of the Royal Society of Queensland</i> 109: 1-30.
  9. Fensham, R.J. and Skull, R.D. 1999. Before cattle: a comparative floristic study of Eucalyptus savanna grazed by macropods and cattle in North Queensland, Australia. <i>Biotropica</i> 31(1): 37-47.
  10. Hunter, J., Kingston, J. and Croft, P. 1999. Vegetation and floristics of Kwambial National Park and surrounds, Ashford, New South Wales. <i>Cunninghamia</i> 6(2): 351-378.
  11. Hunter, J.T. and Clarke, P.J. 1998. The vegetation of granitic outcrop communities on the New England Batholith of eastern Australia. <i>Cunninghamia</i> 5(3): 518-547.
  12. Hosking, J. 1998. Native and exotic flora of the north western slopes upstream of the junction of the Peel and Namoi river, NSW. <i>Cunnighamia</i> 5(3): 721-766.
Évaluateurs & contributeurs (2)Expert
assessor
Romand-Monnier, F.
evaluator
Scott, J.A.

Romand-Monnier, F. 2013. Scleria mackaviensis. The IUCN Red List of Threatened Species 2013: e.T44392831A44429547. Accessed on 05 May 2026.

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

Bibliographie

Note nomenclaturale & synonymesExpert

Note nomenclaturale

TAXREF v18 — INPN/MNHN

Synonymes (2)— redirigent vers cette page

  • Scleria mackaviensis var. atrataDomin
  • Scleria mackaviensis var. pallidaDomin

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