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Eriocaulon carsonii

Eriocaulon carsonii  Photo: EHP

Eriocaulon carsonii Photo: EHP

Scientific name: Eriocaulon carsonii

Family: Eriocaulaceae

Conservation status: Eriocaulon carsonii is listed as Endangered in Queensland (Nature Conservation Act 1992), New South Wales (Threatened Species Conservation Act 1995), South Australia (Australian National Parks and Wildlife Act 1972) and nationally (Environment Protection and Biodiversity Conservation Act 1999). It is ranked as a high priority under the Department of Environment and Heritage Protection Back on Track species prioritisation framework.

Description

E. carsonii is a perennial herb (i.e. it reproduces more than once and lives for more than one year) that has a circular cluster of leaves at its base and clustered flowers that form a tight head. The plant usually forms mat-like colonies and varies in appearance. For example, smaller plants (up to 10 cm tall) with hairless flower heads are found in western Queensland, while larger plants (up to 50 cm tall) with hairy flower heads occur in southern, eastern and northern Queensland. Distinct sub-species have been recognised (Davis et al. 2007).

Habitat and distribution

E. carsonii is only known from spring wetlands fed by permanent groundwater in relatively flat landscapes except for one population which is found in a spring-fed area on the side of a gentle range. In Queensland E. carsonii is known from 12 spring complexes. A spring complex is a group of springs where neighbouring pairs of springs are not more than six kilometres apart and all occur on similar landforms (Fensham & Fairfax 2003). With the exception of two populations in the Einasleigh Uplands region of north Queensland, the Great Artesian Basin sustains the wetlands which support this species. E. carsonii is also recorded from one spring complex in New South Wales and nine in South Australia.

Spring wetlands in the Great Artesian Basin have been well surveyed and there is a high level of certainty that no further complexes containing E. carsonii will be found. Two populations are known to have become extinct as a consequence of Great Artesian Basin springs becoming inactive. One of these populations is in southern Queensland and is in the largest spring of the Eulo region (Wiggera Springs) (Fensham & Fairfax 2003).

Life history and ecology

E. carsonii can establish in suitable habitat within areas where it is known to occur, and is also capable of spreading over large distances. Reproduction is based on the production of abundant tiny seeds that germinate readily. This species is also capable of growth and spread through suckering which forms dense mats.

Threatening processes

Threats to E. carsonii and other native species dependent on natural discharge of groundwater from the Great Artesian Basin include:

  • The artificial removal of groundwater which reduces spring flows into wetlands can leave many spring complexes completely inactive.
  • Damage to spring wetlands through excavation.
  • The introduction of exotic species such as para grass and hymenachne in ponded pastures can compete with and may exclude native plant species from their habitat.
  • Trampling by grazing animals around the edges of spring wetlands which disturbs vegetation and native species populations.
  • The removal and destruction of vegetation by pig rooting (extensive digging to find food such as tubers, worms and soil invertebrates).

Recovery actions

recovery plan for the community of native species dependent on natural discharge of groundwater from the Great Artesian Basin has been developed. The recovery plan sets out actions to benefit the conservation of E. carsonii. These actions include:

  • Minimise impact of stock and feral animal disturbance and manage total grazing pressure. Establish fencing where appropriate including the option to regulate stock use rather than exclude stock.
  • Eradicate exotic plants from springs and ensure no further deliberate introductions of exotic species occur.
  • Effectively monitor spring flows.
  • Ensure landholders understand that excavation and related direct threatening processes are regulated activities.

What can you do to help this species?

  • Avoid excavating spring wetlands containing E. carsonii.
  • Do not plant exotic ponded pasture species or other exotic weed species in spring wetlands.
  • Fence spring wetlands to control stock-use and exclude feral pigs.
  • Do not construct dams that would result in the flooding of springs.
  • Avoid developing new bores for groundwater use or using existing bores that will negatively affect native species populations.

Related information

Davies RJ, Craigie AI, Mackay DA, Whalen MA, Cheong JP, & Leach GL. 2007. Resolution of the taxonomy of Eriocaulon (Eriocaulaceae) taxa endemic to Australian mound springs, using morphometrics and AFLP markers. Australian Systematic Botany, 20(5), 428-447.

Department of Sustainability, Environment, Water, Population and Communities (SEWPaC). 2012. Eriocaulon carsonii salt pipewort, Button grass in the Species Profile and Threats Databse. SEWPaC, Canberra.

Fensham RJ, Ponder WF and Fairfax RJ. 2010. National recovery plan for the community of native species dependent on natural discharge of groundwater from the Great Artesian Basin. Report to the Department of Environment, Water, Heritage and the Arts, Canberra. Queensland Department of Environment and Heritage Protection, Brisbane.

Fensham RJ & Fairfax RJ. 2003. Spring wetlands of the Great Artesian Basin, Queensland, Australia. Wetland Ecology and Management. 11:343-362.

New South Wales National Parks and Wildlife Service. 2002. Salt pipewort (Eriocaulon carsonii) recovery plan. NSW National Parks and Wildlife Service, Hurstville.

Last updated
28 February 2013