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The listed threatened plant taxa within the South Coast Region of New South Wales (Helensburgh to Batemans Bay, as designated by the NSW National Parks and Wildlife Service) are documented. Of the 100 NSW listed taxa, 69 are also listed by the Commonwealth, while two additional taxa are only listed by the Commonwealth. An analysis of the individual taxa and the 62 conservation reserves in the region, found that 30 taxa can with confidence be said to be adequately reserved, while 50 are assessed as inadequately reserved; for the remaining 22 taxa, reservation status is unknown. Examples of challenges for the conservation of threatened plants in the region are examined; these challenges have relevance well beyond the South Coast Region. Managing for individual plant species may be hampered by a lack of basic ecological information; this is particularly so for the rarer species such as orchids. One of the main areas where information is lacking is the response of most species to bushfire. Conservation on private land is becoming an increasingly important and challenging area for plant species conservation as the last large areas of public land are dedicated for one purpose or another. A more co-ordinated approach to conservation on private land may produce improved outcomes for many inadequately reserved taxa.
The terrestrial fern Hypolepis distans (Dennstaedtiaceae) is recorded as indigenous to New Zealand and Tasmania. The fern was not known from New South Wales or the Australian mainland until recently. This paper reports on the recent discovery of the species at Macquarie Pass in the Illawarra area on the south-eastern edge of the Central Tablelands Botanical Subdivision of New South Wales. Its ecology and conservation needs are discussed.
Defining indigenous species may at first appear straight forward; most botanical texts provide similar definitions. The consistent requirement of such definitions is the lack of human intervention in the occurrence of the species within the area under consideration. Islands around the world have been invaded by plant species brought to their shores by humans. They are also places where self-introduced species can be continually arriving, as they have done for millennia. Scrutiny of the situation on Norfolk Island (1200 km east of Australia) finds that the distinction between indigenous and introduced taxa is sometimes unclear. There is also inconsistency regarding the acceptance of self-introduced species as indigenous. This paper explores these issues and notes that they are more important than idle botanical curiosity, because control of introduced (weed) species is a major area of activity in managing protected natural areas.
We establish a methodology and present baseline data for a long-term grassy woodland restoration study that commenced in 2007 in two nature reserves (Mulligans Flat, Goorooyarroo (35° 9–13’ S; 149° 9–12’ E)) totalling 1386 ha on the northern boundary of Canberra, in the Australian Capital Territory in south eastern Australia. The experimental infrastructure comprises 96 × 1 ha sites established in Eucalyptus blakelyi / Eucalyptus melliodora dominated woodland. These are being subjected to varying kangaroo grazing pressure and augmentation with logs, while burning treatments are planned. One reserve (Mulligans Flat) has been fenced for feral predator control and contains half the sites, forming a companion experiment to Goorooyarroo. Our baseline floristic study comprised estimates, at the site level, of ground layer biomass, species biomass, ground cover types and soil (0–10 cm) properties. From these data we conclude that the groundlayer vegetation is dominated by Joycea pallida, Austrodanthonia spp., Themeda australis and Aristida ramosa. These grasses varied in abundance according to differences in soil pH, phosphorus and to a lesser extent nitrates. Forb frequencies were highly sensitive to nitrate levels with annual exotic forbs dominating at high nitrate sites. More generally, soil nutrient levels and exotic species in some sites indicated areas of previous pasture improvement activities. Biomass estimates indicated extremely high grazing pressure, sufficient to negatively affect the habitat quality for ground-dependent fauna and some soil processes. These data will provide an important basis for examining rates of ecosystem recovery under different restoration strategies.
Replacement of Cakile edentula with Cakile maritima in New South Wales and on Lord Howe Island
(2013)
Two species of Cakile (Brassicaceae) have been introduced to Australia and the genus has been a common feature on the beaches of NSW for over 130 years; Cakile edentula has been present for at least 148 years (in NSW since about 1870), while Cakile maritima arrived approximately 114 years ago, (in NSW since about 1969). Collections at CANB and NSW confirm that since around 1970 plants more like Cakile maritima have almost entirely replaced Cakile edentula along the NSW coast. A similar phenomenon is reported for Lord Howe Island.
The occurrence of the coastal ferns Asplenium decurrens and Asplenium difforme (family Aspleniaceae) on the south coast of New South Wales are assessed and discussed. The Illawarra coast was the zone of overlap for these two coastal fern species and they reached their geographical limits in the Kiama area, with Asplenium decurrens reaching its northern limit of distribution and Asplenium difforme reaching its southern limit. All substantiated records of these ferns are documented and assessed. Both species require conservation consideration on the NSW south coast. For Asplenium decurrens the evidence suggests that New South Wales should follow Victoria and list this species as threatened under the Biodiversity Conservation Act 2016 (NSW). For Asplenium difforme local conservation action is needed at its most southern limit at Kiama.
An album of 50 watercolour illustrations depicting Norfolk Island plants attributed to convict artist John Doody, in the early 1790s, and associated notes apparently written by William Paterson (1755-1810), one-time commander of the military detachment on Norfolk Island, Lieutenant Governor of New South Wales, and amateur botanist, are described and assessed. Illustrated are 48 plant species growing on Norfolk Island at the time, all but three of which are indigenous. The notes and the watercolours represent the only treatment of the island's flora in the 18th century and include descriptive and ecological material for the species at the time of first European occupation. Two of the species are now extinct. Paterson's notes also include an introductory description of the flora and fauna of the Island. The importance of this material to the modern study of the Norfolk Island flora is highlighted.
The results of a field survey of Prostanthera tallowa (family Lamiaceae), a rare and only recently described shrub from the lower Shoalhaven River valley, on the NSW South Coast, are described. The extent and size of populations in the vicinity of the type locality at Tallowa Dam are greatly expanded and several new and distant populations are described. Information is provided on all known populations and their habitat. The species is regarded as adequately reserved, as almost all known populations occur in protected areas though the actual area of occupancy is small. The species recruits after fire with most sites having been burnt about 10 years ago; the total known population size is currently over 3,300 plants.
The 2019–20 bushfires in eastern New South Wales were intensive and extensive, with 62% of the native vegetation of the south coast region burnt in a series of large fires. Many of the listed threatened plant species in the region were significantly impacted, including most of the regionally endemic species. This study investigated the responses of two locally endemic mallee species, Eucalyptus langleyi and Eucalyptus sturgissiana (family Myrtaceae) to the fire in the northern Shoalhaven region. A six-month study post-fire found that both species recovered well by vegetative means but recruitment from seedling was apparently absent. A loss 1 – 3% of plants due to fire was recorded from monitored populations. The importance of such a loss to the long-term viability of these species is unknown, especially given the likelihood of more frequent and intense fires in the future.