Cunninghamia : A Journal of Plant Ecology for Eastern Australia, Volume 13 (2013)
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- Barrington Tops (1)
- Cytisus scoparius (1)
- River Sheoak (1)
- broom (1)
- flood disturbance (1)
- fluvial geomorphology (1)
- frost-hollow vegetation (1)
- riparian vegetation (1)
- river training works (1)
- seedling survivorship (1)
The Sicilian endemic herbaceous perennial plant Limonium hyblaeum (family Plumbaginaceae) is rapidly becoming a serious weed in South Australia and Victoria, where it invades saltmarshes and rocky coastal sites exposed to salt spray. It has small, light seeds that float and remain viable in sea water and which can also be dispersed readily by wind, animals and vehicles. It can form dense, extensive mats and buds sprouting from rhizomes allow encroachment into dense native vegetation. It seems certain to be apomictic and is readily able to become dominant. Forming dense, compact cushions which accumulate large amounts of fibrous peat, Limonium hyblaeum is the first cushion plant to become naturalized in Australia; the importance of the cushion habit as an adaptation to salt spray is under-appreciated. Some control measures for Limonium hyblaeum have begun in Victoria, but much remains to be done there and in the other southern Australian states; a ban on the sale of the species by nurseries is urgently required.
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.
To assist with planning and conservation strategies, mapping of wetlands above 700 m elevation across the Namoi Catchment (east of Tamworth) was undertaken. The number of hectares of each type within this high-elevation region, the area currently in conservation reserves and the status of these remnants was assessed. 1 001 wetlands were mapped and allocated to three wetland types (fens, bogs and lagoons) and six disturbance groups (based on agricultural clearing and presence of dams). Total wetlands cover was 4 490 ha, of which fens were the most common, followed by bogs and a single lagoon. The smallest wetland was 0.12 ha in size, the largest 113 ha and the average 5 ha. Only 10% of all wetlands were considered to be in near natural state with only 5.5% of all wetland area protected within conservation reserves.
The exotic shrub Cytisus scoparius (L.) Link (family Fabaceae), known as broom, is having a major impact on native vegetation in naturally treeless sub-alpine frost-hollow areas (c. 32o 01’ 37” S, 151o 26’ 12” E’, 1440 m elevation) at the Barrington Tops, New South Wales, in south-eastern Australia. This vegetation is of limited extent and has significant biogeographical and ecological importance. Nine paired 10 m line transects were compared, with one of the pair in areas of almost 100% Cytisus scoparius and the other in adjacent areas without Cytisus scoparius. Results were compared with species recorded from this area in the 1930s. There are obvious differences in native vegetation in areas with and without Cytisus scoparius. On average there were 5.1 (range 2–10) species per 10 m in areas of almost 100% Cytisus scoparius cover and 17.0 (12–25) species per 10 m in areas adjacent to infested areas but without Cytisus scoparius. Other than Cytisus scoparius, the area surveyed had little in the way of exotic species and these were only present at low densities. Native species present in 2008 are similar to those recorded in the 1930s; there were no records of Cytisus scoparius in the area in the 1930s. The study suggests that control of Cytisus scoparius in naturally treeless areas at the Barrington Tops should be a priority to prevent a decline in the distribution and abundance of many plant species, many of which only occur in treeless areas of the Barrington Tops.
In January 1843, curiosity for natural history led a young German naturalist, Ludwig Leichhardt, to spend about three weeks exploring Mt Royal on the north of the Hunter Valley, about 70 km north west of Newcastle, New South Wales. This was a sidetrack on his journey from Newcastle, through the Hunter Valley and inland to Moreton Bay (Brisbane) and preceded the journeys for which he was to become famous; his 1844–45 overland journey from Moreton Bay to Port Essington (in Northern Territory) and his disappearance without trace in 1848 attempting to cross Australia. Using his Diary and herbarium records this paper brings together the chronological events of the 29 year old Leichhardt’s journey, the plant and animal species recorded, the specimens collected and his landscape descriptions and compares the 1843 landscape with the area today. Most of it is now in Mount Royal National Park, and part of the Gondwana Rainforest Reserves World Heritage Area. Using Mt Royal as an example of the richness of Leichhardt’s scientific legacy, we draw attention to the existence of a considerable number of Leichhardt’s plant specimens in herbaria in Sydney and Melbourne relating to his early collecting around Sydney and the little-known journey from Newcastle to Moreton Bay. Leichhardt’s visit to Mt Royal provides an insight into a gifted young naturalist coping with some of the hardships of nineteenth century botanical exploration, in a landscape which is easily recognizable and of which much is remarkably little changed since European settlement.
The successful management and restoration of riparian corridors in Australia is currently hindered by our poor understanding of the links between hydrology, fluvial geomorphology and plant population dynamics. The aim of the current study was to determine the survival rates of Casuarina cunninghamiana subsp. cunninghamiana Miq. (family Casuarinaceae) on a sand-bed stream in the Wollombi Valley, a tributary of the Hunter River system, in coastal New South Wales (lat 33°02’S; long 151°10’E). A population planted on the banks of Dairy Arm in 1987, as part of river training works, was used to determine the long-term (24-year) survival rate. A bankfull flood in June 2011 provided an opportunity to examine the survival response of seedlings regenerating naturally within the channel. We found that 24% of the seedlings planted on the banks in 1987 had survived to adulthood. The bankfull flood significantly decreased (d.f. = 14; W= - 30; p = 0.0024) median seedling density within the channel from 12 to 2 individuals per 100 m2. Seedling survival varied with height, with seedlings > 15 cm more likely to survive the bankfull flood. The percentage of seedlings partially buried by sediment was significantly higher (d.f. = 14; W = 13; p = 0.016) after flood compared to before flood. Seedling density was positively correlated with the amount of bare ground prior to the flood (r = 0.61; p = 0.02), but this relationship was no longer significant after flood (r = 0.18; p = 0.53). 37% of the seedlings surveyed showed evidence of grazing. Our results confirm that hydrogeomorphic processes associated with a bankfull flood affect the survival of Casuarina cunninghamiana seedlings. The management implications of our findings are discussed in terms of riparian revegetation techniques and the geomorphic recovery of over-widened sand-bed streams.
In this paper we revisit the invasion history of two species of Cakile in Australia. Cakile edentula subsp. edentula arrived in the mid 19th Century and spread into coastal strandline habitat from the southeast towards the west and to the north; Cakile maritima arrived in the late 19th Century and has replaced Cakile edentula over much of the range. While Cakile edentula is morphologically quite uniform, the great variation within Cakile maritima has confused field ecologists. Using herbarium records we update previous accounts of the spread of the species and report on field surveys that determined their current geographic overlap in Tasmania and in northern New South Wales/southern Queensland. We examine regional morphological variation within Cakile maritima using the national herbaria collections and variation within new population samples. We support previous interpretations that Cakile maritima has been introduced on more than one occasion from morphologically distinct races, resulting in regional variation within Australia and high variability within populations in the south-east. Western Australian populations appear distinct and probably did not initiate those in the east; we consider that eastern populations are likely to be a mix of Cakile maritima subsp. maritima from the Mediterranean and Cakile maritima subsp. integrifolia from Atlantic Europe. Although introgression from Cakile edentula into Cakile maritima cannot be discounted from our results, it is not required to explain the levels of variation in the latter species observed in Australia. Cakile maritima continues to spread southwards in Tasmania and northwards in NSW; in Queenland, a recent occurrence has proliferated in Moreton Bay, spreading slowly to the north but not appreciably southwards.
Native vegetation of the upper Murrumbidgee catchment in southeast NSW and the Australian Capital-Territory (ACT) was classified into 75 plant communities across 18 NSW Vegetation Classes within nine Structural-Formations. Plant communities were derived through numerical analysis of 4,106 field survey plots including 3,787-plots from 58 existing survey datasets and 319 new plots, which were sampled in under surveyed ecosystems. All plant-communities are described at a level appropriate for discrimination of threatened ecological communities and distinct-vegetation mapping units.
The classification describes plant communities in the context of the upper Murrumbidgee catchment and surrounding-landscapes of similar ecological character. It incorporates and, in some instances, refines identification of plant-communities described in previous classifications of alpine vegetation, forest ecosystems, woodlands and grasslands-across the Australian Alps and South Eastern Highlands within the upper Murrumbidgee catchment. Altitude,-precipitation, soil saturation, lithology, slope, aspect and landscape position were all important factors in guiding-plant community associations.
Nine Threatened Ecological Communities under Commonwealth, NSW and ACT legislation occur in the upper-Murrumbidgee catchment. This study has also identified five additional plant communities which are highly restricted-in distribution and may require active management or protection to ensure their survival.
The Duck River Reserve and Rookwood Cemetery in the highly urbanised Auburn district of western-Sydney hold small but botanically valuable stands of remnant native vegetation. In the late 1970s, local resident G.A.-(Tony) Price, recognised the value of these remnants, both for the species they held and the clues they could give us-to the past, and spent three years surveying and collecting plants at these sites. Price recorded the species present and-their abundance, and described the habitats in which they were found. He observed the ecology of plant interactions,-moisture, shading and fire response, interpolating them into a picture of the landscape and vegetation of the district-prior to European settlement. At a time when field botany was inaccessible to many, and the focus of conservation was-largely on the broader scale, Price’s local scale work at these sites was unusual and important. Though never formally-published, Price’s 1979 account ‘The Vegetation of Duck River and Rookwood Cemetery, Auburn’ has been cited in-all subsequent work of consequence for the area. This paper presents and reviews Price’s work and discusses his-observations in relation to the current vegetation of these areas. Tony Price’s contributions also highlight the value and-role that ordinary citizens can play alongside professional botanists and plant ecologists in long term data collection,-considered observation and environmental management. A copy of Price’s original unpublished account has been-included as an appendix to this paper.
The distribution, population sizes and habitat preferences of the rare tree ferns Cyathea cunninghamii Hook.f. (Slender Tree Fern) and F1 hybrid Cyathea x marcescens N.A.Wakef. (Skirted Tree Fern) in south-eastern Australia are described, together with the extension of the known distribution range of Cyathea cunninghamii from eastern Victoria into south-eastern New South Wales. Floristic and ecological data, encompassing most of the known habitat types, vegetation associations and population sizes, were collected across 120 locations. Additional information was sought from literature reviews, herbarium collections and field surveys of extant populations.
Cyathea cunninghamii is widespread, with the majority of populations occurring in Tasmania and Victoria, one population in south-eastern NSW and a disjunct population in south-eastern Queensland; Cyathea x marcescens is confined to south and eastern Victoria and south and north eastern Tasmania. Both taxa occur on King Island in Bass Strait. Both taxa have a near coastal distribution with most populations occurring in sub-coastal hinterland and escarpment forests with a median altitude of 288 m. Hierarchical cluster analysis of floristic data across the species’ geographic range identified six vegetation communities ranging from rainforest to damp sclerophyll forest. Their micro-habitat preferences were consistently identified as steeply incised gullies of minor headwater streams of coastal and sub-coastal ranges with a plentiful moisture regime and geomorphic protection from extreme stream flow events, flooding and bank scouring. Sporophyte recruitment was associated with exposed soil of stream banks and edges of constructed walking tracks.
Population sizes of both taxa are small with the majority of populations consisting of less than five adult individuals, with total populations of Cyathea cunninghamii and Cyathea x marcescens estimated at 919 and 221 mature individuals respectively.
Population extinctions in Victoria and Tasmania have primarily been associated with outlier populations in regions subject to agricultural land clearance, habitat modification and changes to fire regimes in crown forests. Nonanthropogenic mortality was associated with land slips, tree falls and stream bank scouring by flood water. Conservation of the hybrid Cyathea x marcescens necessitates the preservation of habitats where both Cyathea cunninghamii and Cyathea australis occur in close proximity to substrates suitable for spore germination. In future, molecular techniques may prove useful for field identification of juvenile stages, facilitating selection of progeny of Cyathea cunninghamii and Cyathea x marcescens for cultivation and re-introduction to sites of previous or possible future extinctions.