Can Oxygen Stable Isotopes Be Used to Track Precipitation Moisture Source in Vascular Plant-Dominated Peatlands? ∗ Matthew J
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Commonwealth Listing Advice on Alpine Sphagnum Bogs And
Advice to the Minister for the Environment, Heritage and the Arts from the Threatened Species Scientific Committee (the Committee) on Amendments to the List of Ecological Communities under the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act) 1. Summary of conservation assessment by the Committee This advice follows the assessment of information provided by a nomination to list the Alpine Bog Community as a threatened ecological community. The nomination was made available for public exhibition and comment for a period of two months. The Committee had regard to all public and expert comments that were relevant to the survival of the ecological community. The Committee judges that the ecological community has been demonstrated to have met sufficient elements of: • Criterion 2 to make it eligible for listing as endangered; • Criterion 3 to make it eligible for listing as endangered; and • Criterion 4 to make it eligible for listing as endangered. 2. Name of the ecological community A nomination was received for the Alpine Bog Community. Alpine bogs are commonly found in the vicinity of alpine fens, and have been identified as being dependent on these (VSAC, 1991a). In order to make identification easier in the field, to recognise the importance of Sphagnum species to alpine bogs, and to acknowledge the interdependency of alpine bogs, fens and the natural drainage lines that connect them, the Committee recommends that the name of the ecological community be changed to the “Alpine Sphagnum Bogs and Associated Fens” ecological community. 3. Description The Alpine Sphagnum Bogs and Associated Fens ecological community generally has sharp boundaries and is easily delineated from other alpine vegetation communities. -
MVG 21 – Other Grasslands, Herblands, Sedgelands and Rushlands
NVIS Fact sheet MVG 21 – Other grasslands, herblands, sedgelands and rushlands Australia’s native vegetation is a rich and fundamental • communities and support a large range of species, partly element of our natural heritage. It binds and nourishes as a result of their geographical range, and variation in our ancient soils; shelters and sustains wildlife, protects soils and site conditions streams, wetlands, estuaries, and coastlines; and absorbs • include many plant species capable of vegetative carbon dioxide while emitting oxygen. The National reproduction by rhizomes, or stolons Vegetation Information System (NVIS) has been developed • can comprise associated species that may include and maintained by all Australian governments to provide perennial forbs or/and short-lived ephemeral plants that a national picture that captures and explains the broad proliferate after seasonal or cyclonic rains, to longer-term diversity of our native vegetation. perennials that rely on underground organs such This is part of a series of fact sheets which the Australian as rhizomes Government developed based on NVIS Version 4.2 data to • occur on a range of sites including intermittently provide detailed descriptions of the major vegetation groups inundated depressions, margins of perennial freshwater (MVGs) and other MVG types. The series is comprised of lagoons and brackish tidal or inland wetlands. Ferns tend a fact sheet for each of the 25 MVGs to inform their use by to dominate specific humid areas where the environment planners and policy makers. An additional eight MVGs are is less variable between seasons available outlining other MVG types. • have structurally distinctive features of landscape that provide a variety of habitats for faunal species For more information on these fact sheets, including its limitations and caveats related to its use, please see: • may be associated with an overstorey of scattered and ‘Introduction to the Major Vegetation Group (MVG) isolated trees fact sheets’. -
Vegetation Benchmarks Rainforest and Related Scrub
Vegetation Benchmarks Rainforest and related scrub Eucryphia lucida Vegetation Condition Benchmarks version 1 Rainforest and Related Scrub RPW Athrotaxis cupressoides open woodland: Sphagnum peatland facies Community Description: Athrotaxis cupressoides (5–8 m) forms small woodland patches or appears as copses and scattered small trees. On the Central Plateau (and other dolerite areas such as Mount Field), broad poorly– drained valleys and small glacial depressions may contain scattered A. cupressoides trees and copses over Sphagnum cristatum bogs. In the treeless gaps, Sphagnum cristatum is usually overgrown by a combination of any of Richea scoparia, R. gunnii, Baloskion australe, Epacris gunnii and Gleichenia alpina. This is one of three benchmarks available for assessing the condition of RPW. This is the appropriate benchmark to use in assessing the condition of the Sphagnum facies of the listed Athrotaxis cupressoides open woodland community (Schedule 3A, Nature Conservation Act 2002). Benchmarks: Length Component Cover % Height (m) DBH (cm) #/ha (m)/0.1 ha Canopy 10% - - - Large Trees - 6 20 5 Organic Litter 10% - Logs ≥ 10 - 2 Large Logs ≥ 10 Recruitment Continuous Understorey Life Forms LF code # Spp Cover % Immature tree IT 1 1 Medium shrub/small shrub S 3 30 Medium sedge/rush/sagg/lily MSR 2 10 Ground fern GF 1 1 Mosses and Lichens ML 1 70 Total 5 8 Last reviewed – 2 November 2016 Tasmanian Vegetation Monitoring and Mapping Program Department of Primary Industries, Parks, Water and Environment http://www.dpipwe.tas.gov.au/tasveg RPW Athrotaxis cupressoides open woodland: Sphagnum facies Species lists: Canopy Tree Species Common Name Notes Athrotaxis cupressoides pencil pine Present as a sparse canopy Typical Understorey Species * Common Name LF Code Epacris gunnii coral heath S Richea scoparia scoparia S Richea gunnii bog candleheath S Astelia alpina pineapple grass MSR Baloskion australe southern cordrush MSR Gleichenia alpina dwarf coralfern GF Sphagnum cristatum sphagnum ML *This list is provided as a guide only. -
Edition 2 from Forest to Fjaeldmark the Vegetation Communities Highland Treeless Vegetation
Edition 2 From Forest to Fjaeldmark The Vegetation Communities Highland treeless vegetation Richea scoparia Edition 2 From Forest to Fjaeldmark 1 Highland treeless vegetation Community (Code) Page Alpine coniferous heathland (HCH) 4 Cushion moorland (HCM) 6 Eastern alpine heathland (HHE) 8 Eastern alpine sedgeland (HSE) 10 Eastern alpine vegetation (undifferentiated) (HUE) 12 Western alpine heathland (HHW) 13 Western alpine sedgeland/herbland (HSW) 15 General description Rainforest and related scrub, Dry eucalypt forest and woodland, Scrub, heathland and coastal complexes. Highland treeless vegetation communities occur Likewise, some non-forest communities with wide within the alpine zone where the growth of trees is environmental amplitudes, such as wetlands, may be impeded by climatic factors. The altitude above found in alpine areas. which trees cannot survive varies between approximately 700 m in the south-west to over The boundaries between alpine vegetation communities are usually well defined, but 1 400 m in the north-east highlands; its exact location depends on a number of factors. In many communities may occur in a tight mosaic. In these parts of Tasmania the boundary is not well defined. situations, mapping community boundaries at Sometimes tree lines are inverted due to exposure 1:25 000 may not be feasible. This is particularly the or frost hollows. problem in the eastern highlands; the class Eastern alpine vegetation (undifferentiated) (HUE) is used in There are seven specific highland heathland, those areas where remote sensing does not provide sedgeland and moorland mapping communities, sufficient resolution. including one undifferentiated class. Other highland treeless vegetation such as grasslands, herbfields, A minor revision in 2017 added information on the grassy sedgelands and wetlands are described in occurrence of peatland pool complexes, and other sections. -
Introduction Methods Results
Papers and Proceedings Royal Society ofTasmania, Volume 1999 103 THE CHARACTERISTICS AND MANAGEMENT PROBLEMS OF THE VEGETATION AND FLORA OF THE HUNTINGFIELD AREA, SOUTHERN TASMANIA by J.B. Kirkpatrick (with two tables, four text-figures and one appendix) KIRKPATRICK, J.B., 1999 (31:x): The characteristics and management problems of the vegetation and flora of the Huntingfield area, southern Tasmania. Pap. Proc. R. Soc. Tasm. 133(1): 103-113. ISSN 0080-4703. School of Geography and Environmental Studies, University ofTasmania, GPO Box 252-78, Hobart, Tasmania, Australia 7001. The Huntingfield area has a varied vegetation, including substantial areas ofEucalyptus amygdalina heathy woodland, heath, buttongrass moorland and E. amygdalina shrubbyforest, with smaller areas ofwetland, grassland and E. ovata shrubbyforest. Six floristic communities are described for the area. Two hundred and one native vascular plant taxa, 26 moss species and ten liverworts are known from the area, which is particularly rich in orchids, two ofwhich are rare in Tasmania. Four other plant species are known to be rare and/or unreserved inTasmania. Sixty-four exotic plantspecies have been observed in the area, most ofwhich do not threaten the native biodiversity. However, a group offire-adapted shrubs are potentially serious invaders. Management problems in the area include the maintenance ofopen areas, weed invasion, pathogen invasion, introduced animals, fire, mechanised recreation, drainage from houses and roads, rubbish dumping and the gathering offirewood, sand and plants. Key Words: flora, forest, heath, Huntingfield, management, Tasmania, vegetation, wetland, woodland. INTRODUCTION species with the most cover in the shrub stratum (dominant species) was noted. If another species had more than half The Huntingfield Estate, approximately 400 ha of forest, the cover ofthe dominant one it was noted as a codominant. -
INDIGENOUS Tube Stocklist 2019 Plants from the Greater Melbourne Area
INDIGENOUS tube stocklist 2019 plants from the greater Melbourne area Kuranga Native Nursery grows an extensive If you are requiring a species not listed, please range of plants which occur naturally in the enquire as it may still be available. Greater Melbourne area. Bushfood plants are We have a range of books for sale which list marked # (refer to details on back page). the indigenous plants of various areas around All plants on this list are grown in 50 mm (2”) Melbourne. square forestry tubes. The seed and All tubes are $2.95 each except those marked cutting material for most of our tube stock with * which are $3.95 each has originated from the Melbourne metropolitan area. 118 York Rd Mt Evelyn Victoria 3796 Tel:9760 8100 www.kuranga.com.au All tubes are $2.95 except those marked with * which are $3.95 each. Total price including GST. # Bushfood plants Bird attracting plants AQUATICS AND BOG PLANTS (located near pond) Baloskion tetraphyllum* Tassel Cord-rush Lovely clump, decorative foliage, reddish/brown tassels Sp-S. Shallow water. Carex appressa Tall Sedge Tussock. 40-60cm x 40-60cm. Yellow/brownish spikelets Sp-S. Moist-wet. Carex breviculmis Short-stem Sedge Tufted sedge 15cm high. Flr spikes Sp-S. Moist depressions to exposed slopes. Carex fascicularis Tassel Sedge Drooping spikelets Sp-S. 1m x 1m. Sun or shade. Pond or bog plant. Carex gaudichaudiana* Tufted Sedge Tufted sedge.10-90cm high. Erect flr spikes Sp-S. Sun, semi-shade. Water’s edge, bog. Carex tasmanica Curly Sedge Tufted sedge to 40cm high. -
Vicariance, Climate Change, Anatomy and Phylogeny of Restionaceae
Botanical Journal of the Linnean Society (2000), 134: 159–177. With 12 figures doi:10.1006/bojl.2000.0368, available online at http://www.idealibrary.com on Under the microscope: plant anatomy and systematics. Edited by P. J. Rudall and P. Gasson Vicariance, climate change, anatomy and phylogeny of Restionaceae H. P. LINDER FLS Bolus Herbarium, University of Cape Town, Rondebosch 7701, South Africa Cutler suggested almost 30 years ago that there was convergent evolution between African and Australian Restionaceae in the distinctive culm anatomical features of Restionaceae. This was based on his interpretation of the homologies of the anatomical features, and these are here tested against a ‘supertree’ phylogeny, based on three separate phylogenies. The first is based on morphology and includes all genera; the other two are based on molecular sequences from the chloroplast genome; one covers the African genera, and the other the Australian genera. This analysis corroborates Cutler’s interpretation of convergent evolution between African and Australian Restionaceae. However, it indicates that for the Australian genera, the evolutionary pathway of the culm anatomy is much more complex than originally thought. In the most likely scenario, the ancestral Restionaceae have protective cells derived from the chlorenchyma. These persist in African Restionaceae, but are soon lost in Australian Restionaceae. Pillar cells and sclerenchyma ribs evolve early in the diversification of Australian Restionaceae, but are secondarily lost numerous times. In some of the reduction cases, the result is a very simple culm anatomy, which Cutler had interpreted as a primitively simple culm type, while in other cases it appears as if the functions of the ribs and pillars may have been taken over by a new structure, protective cells developed from epidermal, rather than chlorenchyma, cells. -
Literaturverzeichnis
Literaturverzeichnis Abaimov, A.P., 2010: Geographical Distribution and Ackerly, D.D., 2009: Evolution, origin and age of Genetics of Siberian Larch Species. In Osawa, A., line ages in the Californian and Mediterranean flo- Zyryanova, O.A., Matsuura, Y., Kajimoto, T. & ras. Journal of Biogeography 36, 1221–1233. Wein, R.W. (eds.), Permafrost Ecosystems. Sibe- Acocks, J.P.H., 1988: Veld Types of South Africa. 3rd rian Larch Forests. Ecological Studies 209, 41–58. Edition. Botanical Research Institute, Pretoria, Abbadie, L., Gignoux, J., Le Roux, X. & Lepage, M. 146 pp. (eds.), 2006: Lamto. Structure, Functioning, and Adam, P., 1990: Saltmarsh Ecology. Cambridge Uni- Dynamics of a Savanna Ecosystem. Ecological Stu- versity Press. Cambridge, 461 pp. dies 179, 415 pp. Adam, P., 1994: Australian Rainforests. Oxford Bio- Abbott, R.J. & Brochmann, C., 2003: History and geography Series No. 6 (Oxford University Press), evolution of the arctic flora: in the footsteps of Eric 308 pp. Hultén. Molecular Ecology 12, 299–313. Adam, P., 1994: Saltmarsh and mangrove. In Groves, Abbott, R.J. & Comes, H.P., 2004: Evolution in the R.H. (ed.), Australian Vegetation. 2nd Edition. Arctic: a phylogeographic analysis of the circu- Cambridge University Press, Melbourne, pp. marctic plant Saxifraga oppositifolia (Purple Saxi- 395–435. frage). New Phytologist 161, 211–224. Adame, M.F., Neil, D., Wright, S.F. & Lovelock, C.E., Abbott, R.J., Chapman, H.M., Crawford, R.M.M. & 2010: Sedimentation within and among mangrove Forbes, D.G., 1995: Molecular diversity and deri- forests along a gradient of geomorphological set- vations of populations of Silene acaulis and Saxi- tings. -
The 1770 Landscape of Botany Bay, the Plants Collected by Banks and Solander and Rehabilitation of Natural Vegetation at Kurnell
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Hochschulschriftenserver - Universität Frankfurt am Main Backdrop to encounter: the 1770 landscape of Botany Bay, the plants collected by Banks and Solander and rehabilitation of natural vegetation at Kurnell Doug Benson1 and Georgina Eldershaw2 1Botanic Gardens Trust, Mrs Macquaries Rd Sydney 2000 AUSTRALIA email [email protected] 2Parks & Wildlife Division, Dept of Environment and Conservation (NSW), PO Box 375 Kurnell NSW 2231 AUSTRALIA email [email protected] Abstract: The first scientific observations on the flora of eastern Australia were made at Botany Bay in April–May 1770. We discuss the landscapes of Botany Bay and particularly of the historic landing place at Kurnell (lat 34˚ 00’ S, long 151˚ 13’ E) (about 16 km south of central Sydney), as described in the journals of Lieutenant James Cook and Joseph Banks on the Endeavour voyage in 1770. We list 132 plant species that were collected at Botany Bay by Banks and Daniel Solander, the first scientific collections of Australian flora. The list is based on a critical assessment of unpublished lists compiled by authors who had access to the collection of the British Museum (now Natural History Museum), together with species from material at National Herbarium of New South Wales that has not been previously available. The list includes Bidens pilosa which has been previously regarded as an introduced species. In 1770 the Europeans set foot on Aboriginal land of the Dharawal people. Since that time the landscape has been altered in response to a succession of different land-uses; farming and grazing, commemorative tree planting, parkland planting, and pleasure ground and tourist visitation. -
4 Chapter Four Recovery of the CO2 Sink in A
http://researchcommons.waikato.ac.nz/ Research Commons at the University of Waikato Copyright Statement: The digital copy of this thesis is protected by the Copyright Act 1994 (New Zealand). The thesis may be consulted by you, provided you comply with the provisions of the Act and the following conditions of use: Any use you make of these documents or images must be for research or private study purposes only, and you may not make them available to any other person. Authors control the copyright of their thesis. You will recognise the author’s right to be identified as the author of the thesis, and due acknowledgement will be made to the author where appropriate. You will obtain the author’s permission before publishing any material from the thesis. Carbon dynamics in restiad peatlands across different timescales A thesis submitted in fulfilment of the requirements for the degree of Doctor of Philosophy in Earth Sciences at The University of Waikato by Joshua Lee Ratcliffe 2019 I would like to dedicate this thesis to my friend and former mentor; Dr. Richard Payne who died in an avalanche on the 26th of May 2019 while attempting to climb an un-named peak upon Nanda Devi mountain. Abstract Peatlands contain one of the largest terrestrial carbon stores on the planet, and one which is known to interact with climate and global biogeochemical cycling of nutrients. Peatlands maintain their carbon primarily through a high and stable water table which restricts decomposition, and large amounts of carbon can be lost upon drying. However, peatlands are also characterised by non-linear responses to external forcing with a complex array of internal feedbacks which tend to dominate ecosystem response over long-timescales and may amplify or dampen external influences. -
Cunninghamia Date of Publication: 18/11/2013 a Journal of Plant Ecology for Eastern Australia
Cunninghamia Date of Publication: 18/11/2013 A journal of plant ecology for eastern Australia ISSN 0727- 9620 (print) • ISSN 2200 - 405X (Online) Impact of broom, Cytisus scoparius (Fabaceae), in naturally treeless sub-alpine frost-hollow vegetation communities at the Barrington Tops, south-eastern Australia John R. Hosking1,3, Mellesa Schroder2 and Bruce McCorkell1 1Tamworth Agricultural Institute, NSW Department of Primary Industries, 4 Marsden Park Road, Calala, NSW 2340 AUSTRALIA. email [email protected] 2NSW Office of Environment and Heritage, National Parks and Wildlife Service, corner of Kosciusko Way and Thredbo Terrace, Jindabyne, NSW 2627 AUSTRALIA. email [email protected] 3current address: NCW Beadle Herbarium, University of New England, Armidale, NSW 2351 AUSTRALIA. email [email protected] Abstract: 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. -
Report on the Grimwade Plant Collection of Percival St John and Botanical Exploration of Mt Buffalo National Park (Victoria, Australia)
Report on the Grimwade Plant Collection of Percival St John and Botanical Exploration of Mt Buffalo National Park (Victoria, Australia) Alison Kellow Michael Bayly Pauline Ladiges School of Botany, The University of Melbourne July, 2007 THE GRIMWADE PLANT COLLECTION, MT BUFFALO Contents Summary ...........................................................................................................................3 Mt Buffalo and its flora.....................................................................................................4 History of botanical exploration........................................................................................5 The Grimwade plant collection of Percival St John..........................................................8 A new collection of plants from Mt Buffalo - The Miegunyah Plant Collection (2006/2007) ....................................................................................................................................13 Plant species list for Mt Buffalo National Park...............................................................18 Conclusion.......................................................................................................................19 Acknowledgments...........................................................................................................19 References .......................................................................................................................20 Appendix 1 Details of specimens in the Grimwade Plant Collection.............................22