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December 8-10Am Fancy, and My Camera Thank Goodness Because the Subsequent Years Produced None Or Hardly Any Orchids
W: https://austplants.com.au/Southern-Tablelands E: [email protected] ACN 002 680 408 N E W S L E T T E R D E C E M B E R 2020 ROTARY MARKETS PLANT SALE dentata; occasional specimens of Dampiera stricta also provided blue colour. This was held a few weeks back and was our first plant sale in just over The tall sedge, Lepidosperma neesii was widespread and very 12 months. It also turned out to be our most lucrative sale with the profit healthy looking. We saw one burnt specimen of Melaleuca making its way into four figures. From the moment we had the ‘tent’ in hypericifolia which can display red ‘bottlebrush’ flowers; no flowers place we were besieged by buyers who seemed to know what they on this specimen - just some leaves and some seed pods to wanted. In the Riversdale sale last year, a number of buyers had been identify it. attracted by the display of the large ‘billy buttons - Pycnosorus The new growth did not make some plant identifications easier. globosus. While we had a few of those at the recent sale, they did not We are generally used to identifying species when they are mature attract much attention. It is likely of course that the success of the sale specimens. With re-growth, floral parts are often missing thus is at least partly related to the current situation in society; there is some leaving a vital clue out of the picture. belief that people want to get out and do things once again. -
The Relation Between Road Crack Vegetation and Plant Biodiversity in Urban Landscape
Int. J. of GEOMATE, June, 2014, Vol. 6, No. 2 (Sl. No. 12), pp. 885-891 Geotech., Const. Mat. & Env., ISSN:2186-2982(P), 2186-2990(O), Japan THE RELATION BETWEEN ROAD CRACK VEGETATION AND PLANT BIODIVERSITY IN URBAN LANDSCAPE Taizo Uchida1, JunHuan Xue1,2, Daisuke Hayasaka3, Teruo Arase4, William T. Haller5 and Lyn A. Gettys5 1Faculty of Engineering, Kyushu Sangyo University, Japan; 2Suzhou Polytechnic Institute of Agriculture, China; 3Faculty of Agriculture, Kinki University, Japan; 4Faculty of Agriculture, Shinshu University, Japan; 5Center for Aquatic and Invasive Plants, University of Florida, USA ABSTRACT: The objective of this study is to collect basic information on vegetation in road crack, especially in curbside crack of road, for evaluating plant biodiversity in urban landscape. A curbside crack in this study was defined as a linear space (under 20 mm in width) between the asphalt pavement and curbstone. The species composition of plants invading curbside cracks was surveyed in 38 plots along the serial National Route, over a total length of 36.5 km, in Fukuoka City in southern Japan. In total, 113 species including native plants (83 species, 73.5%), perennial herbs (57 species, 50.4%) and woody plants (13 species, 11.5%) were recorded in curbside cracks. Buried seeds were also obtained from soil in curbside cracks, which means the cracks would possess a potential as seed bank. Incidentally, no significant differences were found in the vegetation characteristics of curbside cracks among land-use types (Kolmogorov-Smirnov Test, P > 0.05). From these results, curbside cracks would be likely to play an important role in offering habitat for plants in urban area. -
Chemical Constituents from Flueggea Virosa and the Structural Revision of Dehydrochebulic Acid Trimethyl Ester
molecules Article Chemical Constituents from Flueggea virosa and the Structural Revision of Dehydrochebulic Acid Trimethyl Ester Chih-Hua Chao 1,2,*, Ying-Ju Lin 3,4, Ju-Chien Cheng 5, Hui-Chi Huang 6, Yung-Ju Yeh 5, Tian-Shung Wu 7,8, Syh-Yuan Hwang 9 and Yang-Chang Wu 1,2,10,11,* 1 School of Pharmacy, China Medical University, Taichung 40402, Taiwan 2 Chinese Medicine Research and Development Center, China Medical University Hospital, Taichung 40447, Taiwan 3 School of Chinese Medicine, China Medical University, Taichung 40402, Taiwan; [email protected] 4 Genetic Center, Department of Medical Research, China Medical University Hospital, Taichung 40447, Taiwan 5 Department of Medical Laboratory Science and Biotechnology, China Medical University, Taichung 40402, Taiwan; [email protected] (J.-C.C.); [email protected] (Y.-J.Y.) 6 Department of Chinese Pharmaceutical Sciences and Chinese Medicine Resources, China Medical University, Taichung 40402, Taiwan; [email protected] 7 Department of Pharmacy, National Cheng Kung University, Tainan 70101, Taiwan; [email protected] 8 Department of Pharmacy and Graduate Institute of Pharmaceutical Technology, Tajen University, Pingtung 90741, Taiwan 9 Endemic Species Research Institute, Council of Agriculture, Nantou 55244, Taiwan; [email protected] 10 Center for Molecular Medicine, China Medical University Hospital, Taichung 40447, Taiwan 11 Graduate Institute of Natural Products, Kaohsiung Medical University, Kaohsiung 80708, Taiwan * Correspondence: [email protected] (C.-H.C.); [email protected] (Y.-C.W.); Tel.: +886-4-2205-3366 (ext. 5157) (C.-H.C.) Academic Editor: Derek J. McPhee Received: 9 August 2016; Accepted: 12 September 2016; Published: 16 September 2016 Abstract: In an attempt to study the chemical constituents from the twigs and leaves of Flueggea virosa, a new terpenoid, 9(10!20)-abeo-ent-podocarpane, 3β,10α-dihydroxy-12-methoxy-13- methyl-9(10!20)-abeo-ent-podocarpa-6,8,11,13-tetraene (1), as well as five known compounds were characterized. -
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. -
New Jan16.2011
Spring 2011 Mail Order Catalog Cistus Nursery 22711 NW Gillihan Road Sauvie Island, OR 97231 503.621.2233 phone 503.621.9657 fax order by phone 9 - 5 pst, visit 10am - 5pm, fax, mail, or email: [email protected] 24-7-365 www.cistus.com Spring 2011 Mail Order Catalog 2 USDA zone: 2 Symphoricarpos orbiculatus ‘Aureovariegatus’ coralberry Old fashioned deciduous coralberry with knock your socks off variegation - green leaves with creamy white edges. Pale white-tinted-pink, mid-summer flowers attract bees and butterflies and are followed by bird friendly, translucent, coral berries. To 6 ft or so in most any normal garden conditions - full sun to part shade with regular summer water. Frost hardy in USDA zone 2. $12 Caprifoliaceae USDA zone: 3 Athyrium filix-femina 'Frizelliae' Tatting fern An unique and striking fern with narrow fronds, only 1" wide and oddly bumpy along the sides as if beaded or ... tatted. Found originally in the Irish garden of Mrs. Frizell and loved for it quirkiness ever since. To only 1 ft tall x 2 ft wide and deciduous, coming back slowly in spring. Best in bright shade or shade where soil is rich. Requires summer water. Frost hardy to -40F, USDA zone 3 and said to be deer resistant. $14 Woodsiaceae USDA zone: 4 Aralia cordata 'Sun King' perennial spikenard The foliage is golden, often with red stems, and dazzling on this big and bold perennial, quickly to 3 ft tall and wide, first discovered in a department store in Japan by nurseryman Barry Yinger. Spikes of aralia type white flowers in summer are followed by purple-black berries. -
Kosipe Revisited
Peat in the mountains of New Guinea G.S. Hope Department of Archaeology and Natural History, Australian National University, Canberra, Australia _______________________________________________________________________________________ SUMMARY Peatlands are common in montane areas above 1,000 m in New Guinea and become extensive above 3,000 m in the subalpine zone. In the montane mires, swamp forests and grass or sedge fens predominate on swampy valley bottoms. These mires may be 4–8 m in depth and up to 30,000 years in age. In Papua New Guinea (PNG) there is about 2,250 km2 of montane peatland, and Papua Province (the Indonesian western half of the island) probably contains much more. Above 3,000 m, peat soils form under blanket bog on slopes as well as on valley floors. Vegetation types include cushion bog, grass bog and sedge fen. Typical peat depths are 0.5‒1 m on slopes, but valley floors and hollows contain up to 10 m of peat. The estimated total extent of mountain peatland is 14,800 km2 with 5,965 km2 in PNG and about 8,800 km2 in Papua Province. The stratigraphy, age structure and vegetation histories of 45 peatland or organic limnic sites above 750 m have been investigated since 1965. These record major vegetation shifts at 28,000, 17,000‒14,000 and 9,000 years ago and a variable history of human disturbance from 14,000 years ago with extensive clearance by the mid- Holocene at some sites. While montane peatlands were important agricultural centres in the Holocene, the introduction of new dryland crops has resulted in the abandonment of some peatlands in the last few centuries. -
Alpine Sphagnum Bogs and Associated Fens
Alpine Sphagnum Bogs and Associated Fens A nationally threatened ecological community Environment Protection and Biodiversity Conservation Act 1999 Policy Statement 3.16 This brochure is designed to assist land managers, owners and occupiers to identify, assess and manage the Alpine Sphagnum Bogs and Associated Fens, an ecological community listed under Australia’s national environment law, the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act). The brochure is a companion document to the listing advice which can be found at the Australian Government’s Species Profile and Threats Database (SPRAT). Please go to the Alpine Sphagnum Bogs and Associated Fens ecological community profile in SPRAT, then click on the ‘Details’ link: www.environment.gov.au/cgi-bin/sprat/public/publiclookupcommunities.pl • The Alpine Sphagnum Bogs and Associated Fens ecological community is found in small pockets in the high country of Tasmania, Victoria, New South Wales and the Australian Capital Territory. • The Alpine Sphagnum Bogs and Associated Fens ecological community can usually be defined by the presence or absence of sphagnum moss. • Long term conservation and restoration of this ecological community is essential in order to protect vital inland water resources. • Implementing favourable land use and management practices is encouraged at sites containing this ecological community. Disclaimer The contents of this document have been compiled using a range of source materials. This document is valid as at August 2009. The Commonwealth Government is not liable for any loss or damage that may be occasioned directly or indirectly through the use of or reliance on the contents of the document. © Commonwealth of Australia 2009 This work is copyright. -
GENOME EVOLUTION in MONOCOTS a Dissertation
GENOME EVOLUTION IN MONOCOTS A Dissertation Presented to The Faculty of the Graduate School At the University of Missouri In Partial Fulfillment Of the Requirements for the Degree Doctor of Philosophy By Kate L. Hertweck Dr. J. Chris Pires, Dissertation Advisor JULY 2011 The undersigned, appointed by the dean of the Graduate School, have examined the dissertation entitled GENOME EVOLUTION IN MONOCOTS Presented by Kate L. Hertweck A candidate for the degree of Doctor of Philosophy And hereby certify that, in their opinion, it is worthy of acceptance. Dr. J. Chris Pires Dr. Lori Eggert Dr. Candace Galen Dr. Rose‐Marie Muzika ACKNOWLEDGEMENTS I am indebted to many people for their assistance during the course of my graduate education. I would not have derived such a keen understanding of the learning process without the tutelage of Dr. Sandi Abell. Members of the Pires lab provided prolific support in improving lab techniques, computational analysis, greenhouse maintenance, and writing support. Team Monocot, including Dr. Mike Kinney, Dr. Roxi Steele, and Erica Wheeler were particularly helpful, but other lab members working on Brassicaceae (Dr. Zhiyong Xiong, Dr. Maqsood Rehman, Pat Edger, Tatiana Arias, Dustin Mayfield) all provided vital support as well. I am also grateful for the support of a high school student, Cady Anderson, and an undergraduate, Tori Docktor, for their assistance in laboratory procedures. Many people, scientist and otherwise, helped with field collections: Dr. Travis Columbus, Hester Bell, Doug and Judy McGoon, Julie Ketner, Katy Klymus, and William Alexander. Many thanks to Barb Sonderman for taking care of my greenhouse collection of many odd plants brought back from the field. -
Supporting Information Appendix Pliocene Reversal of Late Neogene
1 Supporting Information Appendix 2 Pliocene reversal of late Neogene aridification 3 4 J.M.K. Sniderman, J. Woodhead, J. Hellstrom, G.J. Jordan, R.N. Drysdale, J.J. Tyler, N. 5 Porch 6 7 8 SUPPLEMENTARY MATERIALS AND METHODS 9 10 Pollen analysis. We attempted to extract fossil pollen from 81 speleothems collected from 11 16 caves from the Western Australian portion of the Nullarbor Plain. Nullarbor speleothems 12 and caves are essentially “fossil” features that appear to have been preserved by very slow 13 rates of landscape change in a semi-arid landscape. Sample collection targeted fallen, well 14 preserved speleothems in multiple caves. U-Pb dates of these speleothems (Table S3) 15 ranged from late Miocene (8.19 Ma) to Middle Pleistocene (0.41 Ma), with an average age 16 of 4.11 Ma. 17 Fossil pollen typically is present in speleothems in very low concentrations, so pollen 18 processing techniques were developed to minimize contamination by modern pollen (1), but 19 also to maximize recovery, to accommodate the highly variable organic matter content of the 20 speleothems, and to remove a clay- to fine silt-sized mineral fraction present in many 21 samples, which was resistant to cold HF and which can become electrostatically attracted to 22 pollen grains, inhibiting their identification. Stalagmite and flowstone samples of 30-200 g 23 mass were first cut on a diamond rock saw in order to remove any obviously porous material. 24 All subsequent physical and chemical processes were carried out within a HEPA-filtered 25 exhausting clean air cabinet in an ISO Class 7 clean room. -
ACT, Australian Capital Territory
Biodiversity Summary for NRM Regions Species List What is the summary for and where does it come from? This list has been produced by the Department of Sustainability, Environment, Water, Population and Communities (SEWPC) for the Natural Resource Management Spatial Information System. The list was produced using the AustralianAustralian Natural Natural Heritage Heritage Assessment Assessment Tool Tool (ANHAT), which analyses data from a range of plant and animal surveys and collections from across Australia to automatically generate a report for each NRM region. Data sources (Appendix 2) include national and state herbaria, museums, state governments, CSIRO, Birds Australia and a range of surveys conducted by or for DEWHA. For each family of plant and animal covered by ANHAT (Appendix 1), this document gives the number of species in the country and how many of them are found in the region. It also identifies species listed as Vulnerable, Critically Endangered, Endangered or Conservation Dependent under the EPBC Act. A biodiversity summary for this region is also available. For more information please see: www.environment.gov.au/heritage/anhat/index.html Limitations • ANHAT currently contains information on the distribution of over 30,000 Australian taxa. This includes all mammals, birds, reptiles, frogs and fish, 137 families of vascular plants (over 15,000 species) and a range of invertebrate groups. Groups notnot yet yet covered covered in inANHAT ANHAT are notnot included included in in the the list. list. • The data used come from authoritative sources, but they are not perfect. All species names have been confirmed as valid species names, but it is not possible to confirm all species locations. -
Ophiopogon Japonicus -- Mondo Grass Page 2
Fact Sheet FPS-446 October, 1999 Ophiopogon japonicus1 Edward F. Gilman2 Introduction Mondo Grass has many attributes which continue to make it a popular groundcover (Fig. 1). The dark green, six to 8- inch-tall, grasslike mounds are comprised of amazingly sturdy plants, tolerating full sun (except in the Deep South) to deep shade, drought or periods of standing water, an ability to tolerate some foot traffic, and a seeming immunity to most insect pests or diseases. General Information Scientific name: Ophiopogon japonicus Pronunciation: oh-fee-oh-POE-gawn juh-PAWN-nick-kuss Common name(s): Mondo Grass, Dwarf Lilyturf Family: Liliaceae Plant type: perennial; herbaceous; ornamental grass USDA hardiness zones: 7 through 11 (Fig. 2) Planting month for zone 7: year round Planting month for zone 8: year round Planting month for zone 9: year round Planting month for zone 10 and 11: year round Figure 1. Mondo Grass. Origin: not native to North America Uses: mass planting; edging Plant density: dense Availablity: generally available in many areas within its Growth rate: slow hardiness range Texture: fine Description Foliage Height: .3 to .7 feet Spread: depends upon supporting structure Leaf arrangement: most emerge from the soil, usually without Plant habit: spreading a stem 1.This document is Fact Sheet FPS-446, one of a series of the Environmental Horticulture Department, Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of Florida. Publication date: October, 1999 Please visit the EDIS Web site at http:/edis.ifas.ufl.edu. 2. Edward F. Gilman, professor, Environmental Horticulture Department, Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of Florida, Gainesville, 32611.