Studies on the Biomass, Diversity and Nutrient Relationships of Macroalgae and Seagrasses in Lake Illawarra, New South Wales, Australia

Total Page:16

File Type:pdf, Size:1020Kb

Studies on the Biomass, Diversity and Nutrient Relationships of Macroalgae and Seagrasses in Lake Illawarra, New South Wales, Australia University of Wollongong Theses Collection University of Wollongong Theses Collection University of Wollongong Year Studies on the biomass, diversity and nutrient relationships of macroalgae and seagrasses in Lake Illawarra, New South Wales, Australia Karin Rutten University of Wollongong Rutten, Karin, Studies on the biomass, diversity and nutrient relationships of macroalgae and seagrasses in Lake Illawarra, New South Wales, Australia, PhD thesis, School of Earth and Environmental Sciences, University of Wollongong, 2007. http://ro.uow.edu.au/theses/22 This paper is posted at Research Online. http://ro.uow.edu.au/theses/22 Studies on the biomass, diversity and nutrient relationships of macroalgae and seagrasses in Lake Illawarra, New South Wales, Australia A thesis submitted in fulfillment of the requirements for the award of the degree DOCTOR OF PHILOSOPHY from UNIVERSITY OF WOLLONGONG by KARIN RUTTEN SCHOOL OF EARTH AND ENVIRONMENTAL SCIENCES - 2007 - Thesis Declaration I, Karin Rutten, declare that this thesis, submitted in fulfillment of the requirements for the award of Doctor of Philosophy, in the School of Earth and Environmental Sciences, University of Wollongong, is wholly my own work unless otherwise referenced or acknowledged. The document has not been submitted for qualifications at any other institution. Karin Rutten - II - Table of Contents Thesis Declaration ........................................................................................................................ II Table of Contents......................................................................................................................... III List of Figures.............................................................................................................................. VII List of Tables................................................................................................................................. X List of Plates...............................................................................................................................XIV Abstract ......................................................................................................................................XVI Publications arising to date from this study..............................................................................XVIII Acknowledgements ..................................................................................................................XVIII CHAPTER 1 Introduction ......................................................................................................1 1.1 General Introduction..........................................................................................................1 1.2 Statement of the Problem .................................................................................................2 1.3 Thesis Aims and Objectives..............................................................................................3 1.4 Thesis Outline ...................................................................................................................3 1.5 Study Site - Lake Illawarra ................................................................................................4 1.5.1 Site Description ................................................................................................. 4 1.5.2 Catchment Land Use ........................................................................................ 4 1.5.3 Climate .............................................................................................................. 6 1.5.4 Lake Entrance Conditions ................................................................................. 7 1.5.5 Nutrient Enrichment........................................................................................... 8 1.5.6 Macroalgal Blooms.......................................................................................... 11 1.5.7 Macroalgal Harvesting .................................................................................... 12 1.6 Summary.........................................................................................................................13 CHAPTER 2 Literature Review ...........................................................................................14 2.1 Introduction .....................................................................................................................14 2.2 Ecology of Aquatic Macrophytes.....................................................................................15 2.2.1 Seagrasses ..................................................................................................... 16 2.2.2 Macroalgae...................................................................................................... 18 2.2.3 Macrophyte Biomass....................................................................................... 20 2.2.4 Environmental Limitations on Macrophyte Growth ......................................... 21 2.3 Photosynthesis in Aquatic Macrophytes .........................................................................23 2.3.1 Availability of Light........................................................................................... 24 2.3.2 Carbon............................................................................................................. 27 2.4 Nutrients..........................................................................................................................30 2.4.1 Nutrients Required by Macrophytes................................................................ 31 2.4.2 The Phosphorus Cycle.................................................................................... 32 2.4.3 The Nitrogen Cycle.......................................................................................... 34 2.5 Nutrient Uptake by Macrophytes.....................................................................................36 2.5.1 Phosphorus Uptake......................................................................................... 37 2.5.2 Nitrogen Uptake .............................................................................................. 37 2.5.3 Growth of Macroalgae in Culture .................................................................... 38 2.5.4 Nutrient Uptake Kinetics.................................................................................. 39 2.5.5 Nutrient Limitation ........................................................................................... 43 2.5.6 Nutrient Uptake from Sediment....................................................................... 44 2.5.7 Factors Affecting Nutrient Uptake ................................................................... 45 2.6 Macrophyte Tissue Nutrient Concentrations...................................................................46 2.6.1 Effect of Nutrient Enrichment .......................................................................... 51 - III - 2.6.2 Stoichiometric Ratios of C : N : P.................................................................... 52 2.6.3 Stable Isotopes of C and N ............................................................................. 55 2.7 Local Macrophyte Studies...............................................................................................59 CHAPTER 3 Materials and Methods ..................................................................................60 3.1 Introduction .....................................................................................................................60 3.2 Methodology used for the Studies of Macrophyte Biomass, Distribution and Diversity in Lake Illawarra ...................................................................................................................60 3.2.1 Site Selection .................................................................................................. 60 3.2.2 Sample Collection and Preservation............................................................... 61 3.2.3 Macrophyte Sample Preparation..................................................................... 63 3.2.4 Identification of Macrophytes .......................................................................... 63 3.2.5 Sediment Sample Preparation ........................................................................ 64 3.2.6 External Laboratory Analysis and Quality Control Samples ........................... 64 3.2.7 Statistical Analyses ......................................................................................... 66 3.3 Methodology used for the Experimental Growth in Culture of Chaetomorpha linum .....67 3.3.1 Sample Collection ........................................................................................... 67 3.3.2 Preconditioning and Culture Media................................................................. 67 3.3.3 Media Preparation........................................................................................... 69 3.3.4 Experimental Apparatus.................................................................................. 70 3.3.5 Preparation of Plant Material........................................................................... 70 3.3.6 Experimental Design ....................................................................................... 71 3.3.7 Calculations and Statistics .............................................................................
Recommended publications
  • Global Seagrass Distribution and Diversity: a Bioregional Model ⁎ F
    Journal of Experimental Marine Biology and Ecology 350 (2007) 3–20 www.elsevier.com/locate/jembe Global seagrass distribution and diversity: A bioregional model ⁎ F. Short a, , T. Carruthers b, W. Dennison b, M. Waycott c a Department of Natural Resources, University of New Hampshire, Jackson Estuarine Laboratory, Durham, NH 03824, USA b Integration and Application Network, University of Maryland Center for Environmental Science, Cambridge, MD 21613, USA c School of Marine and Tropical Biology, James Cook University, Townsville, 4811 Queensland, Australia Received 1 February 2007; received in revised form 31 May 2007; accepted 4 June 2007 Abstract Seagrasses, marine flowering plants, are widely distributed along temperate and tropical coastlines of the world. Seagrasses have key ecological roles in coastal ecosystems and can form extensive meadows supporting high biodiversity. The global species diversity of seagrasses is low (b60 species), but species can have ranges that extend for thousands of kilometers of coastline. Seagrass bioregions are defined here, based on species assemblages, species distributional ranges, and tropical and temperate influences. Six global bioregions are presented: four temperate and two tropical. The temperate bioregions include the Temperate North Atlantic, the Temperate North Pacific, the Mediterranean, and the Temperate Southern Oceans. The Temperate North Atlantic has low seagrass diversity, the major species being Zostera marina, typically occurring in estuaries and lagoons. The Temperate North Pacific has high seagrass diversity with Zostera spp. in estuaries and lagoons as well as Phyllospadix spp. in the surf zone. The Mediterranean region has clear water with vast meadows of moderate diversity of both temperate and tropical seagrasses, dominated by deep-growing Posidonia oceanica.
    [Show full text]
  • Seed Selection and Storage with Nano-Silver and Copper As
    www.nature.com/scientificreports OPEN Seed selection and storage with nano-silver and copper as potential antibacterial agents for the seagrass Zostera marina: implications for habitat restoration Shaochun Xu1,2,3, Yi Zhou1,2,4*, Shuai Xu1,2,3, Ruiting Gu1,2,3, Shidong Yue1,2,3, Yu Zhang1,2,3 & Xiaomei Zhang1,2,4 Globally, seagrass meadows are extremely important marine ecosystems that are disappearing at an alarming rate. Therefore, research into seagrass restoration has become increasingly important. Various strategies have been used in Zostera marina L. (eelgrass) restoration, including planting seeds. To improve the efciency of restoration by planting seeds, it is necessary to select high-quality seeds. In addition, a suitable antibacterial agent is necessary for wet storage of desiccation sensitive seeds to reduce or inhibit microorganism infection and seed decay. In the present study, an efcient method for selecting for high-quality eelgrass seeds using diferent specifc gravities of salt water was developed, and potential antibacterial agents (nano-silver and copper sulfate) for seed storage were assessed. The results showed that the highest proportion of intact seeds (72.91 ± 0.50%) was recorded at specifc gravities greater than 1.20. Therefore, specifc gravities greater than 1.20 can be used for selecting high-quality eelgrass seeds. During seed storage at 0 °C, the proportion of intact seeds after storage with nano-silver agent was over 90%, and also higher than 80% with copper sulfate agent, which was signifcantly higher than control treatments. The fndings revealed a potential selection method for high-quality seeds and long-term seed storage conditions for Z.
    [Show full text]
  • Macrobrachium Intermedium in Southeastern Australia: Spatial Heterogeneity and the Effects of Species of Seagrass
    MARINE ECOLOGY PROGRESS SERIES Vol. 75: 239-249, 1991 Published September 11 Mar. Ecol. Prog. Ser. Demographic patterns of the palaemonid prawn Macrobrachium intermedium in southeastern Australia: spatial heterogeneity and the effects of species of seagrass Charles A. Gray* School of Biological Sciences, University of Sydney, 2006, NSW. Australia ABSTRACT. The effects of species of seagrass (Zostera capricorni and Posidonia australis) on spatial and temporal heterogeneity in the demography of estuarine populations of the palaemonid prawn Macrobrachium intermedium across 65 km of the Sydney region, southeastern Australia, were examined. Three estuaries were sampled in 1983 and 1984 to assess the magnitude of intra- and inter- estuary variability in demographic characteristics among populations. Species of seagrass had no effect on the demographic patterns of populations: differences in the magnitude and directions of change in abundances, recruitment, reproductive characteristics, size structures and growth were as great among populations within each species of seagrass as those between the 2 seagrasses Abiotic factors, such as the location of a meadow in relation to depth of water and distance offshore, and the interactions of these factors with recruiting larvae are hypothesised to have greater influence than the species of seagrass in determining the distribution and abundance of these prawns. Spatial and temporal heterogeneity in demography was similar across all spatial scales sampled: among meadows (50 m to 3 km apart) in an estuary and among meadows in all 3 estuaries (10 to 65 km apart). Variability in demographic processes among populations in the Sydney region was most likely due to stochastic factors extrinsic to the seagrasses then~selves.I conclude that the demography of seagrass-dwelling estuarine populations of M.
    [Show full text]
  • Seagrass Habitats of Northeast Australia: Models of Key Processes and Controls
    BULLETIN OF MARINE SCIENCE, 71(3): 1153–1169, 2002 SEAGRASS HABITATS OF NORTHEAST AUSTRALIA: MODELS OF KEY PROCESSES AND CONTROLS T. J. B. Carruthers, W. C. Dennison, B. J. Longstaff, M. Waycott, E. G. Abal, L. J. McKenzie and W. J. Lee Long ABSTRACT An extensive and diverse assemblage of seagrass habitats exists along the tropical and subtropical coastline of north east Australia and the associated Great Barrier Reef. In their natural state, these habitats are characterised by very low nutrient concentrations and are primarily nitrogen limited. Summer rainfall and tropical storms/cyclones lead to large flows of sediment-laden fresh water. Macro grazers, dugongs (Dugong dugon) and green sea turtles (Chelonia mydas) are an important feature in structuring tropical Aus- tralian seagrass communities. In general, all seagrass habitats in north east Australia are influenced by high disturbance and are both spatially and temporally variable. This pa- per classifies the diversity into four habitat types and proposes the main limiting factor for each habitat. The major processes that categorise each habitat are described and sig- nificant threats or gaps in understanding are identified. Four broad categories of seagrass habitat are defined as ‘River estuaries’, ‘Coastal’, ‘Deep water’ and ‘Reef’, and the domi- nant controlling factors are terrigenous runoff, physical disturbance, low light and low nutrients, respectively. Generic concepts of seagrass ecology and habitat function have often been found inappropriate to the diverse range of seagrass habitats in north east Australian waters. The classification and models developed here explain differences in habitats by identifying ecological functions and potential response to impacts in each habitat.
    [Show full text]
  • Anthropogenic Impacts on Waituna Lagoon: Reconstructing The
    i Anthropogenic impacts on Waituna Lagoon: Reconstructing the environmental history Sarai Cosgrove 2011 A dissertation submitted in partial fulfilment of the requirements for a Master of Science degree in Ecology at the University of Otago, Dunedin, New Zealand ii iii Abstract Waituna Lagoon is a shallow temperate coastal lagoon in Southland, New Zealand. The 1,350 hectare Waituna Lagoon and associated wetland system is of national and international importance for its unique ecology and the cultural values placed upon it. Waituna is opened to the sea ca. 1-2 times annually, during which time it becomes estuarine. This opening regime has been artificially managed since 1908, with an unknown impact on the lagoon. Since 2007, Waituna appears to have experienced rapid degradation and eutrophication, possibly due to intensification of farming in its catchment. It has rare, extensive beds of the seagrasses Ruppia megacarpa and Ruppia polycarpa, which have been lost from many similar systems due to eutrophication and sedimentation. Waituna Lagoon is currently under active management to preserve its unique ecology, and its restoration to a more natural state is being considered. This study aims to reconstruct Waituna Lagoon’s natural opening regime and Ruppia dynamics, as understanding the natural ecosystem is important for restoration. The hypotheses are: (1) that under a natural opening regime, environmental variations within Waituna Lagoon were less frequent but more extreme; (2) that Ruppia was not present in Waituna Lagoon under a natural opening regime; and (3) that Ruppia was not dominant in Waituna Lagoon under a natural opening regime. Three push cores (130, 83 and 64 cm length) were collected from the sheltered Shand Bay and from the wind-exposed, deepest site in the main lagoon.
    [Show full text]
  • 1 Phylogenetic Regionalization of Marine Plants Reveals Close Evolutionary Affinities Among Disjunct Temperate Assemblages Barna
    Phylogenetic regionalization of marine plants reveals close evolutionary affinities among disjunct temperate assemblages Barnabas H. Darua,b,*, Ben G. Holtc, Jean-Philippe Lessardd,e, Kowiyou Yessoufouf and T. Jonathan Daviesg,h aDepartment of Organismic and Evolutionary Biology and Harvard University Herbaria, Harvard University, Cambridge, MA 02138, USA bDepartment of Plant Science, University of Pretoria, Private Bag X20, Hatfield 0028, Pretoria, South Africa cDepartment of Life Sciences, Imperial College London, Silwood Park Campus, Ascot SL5 7PY, United Kingdom dQuebec Centre for Biodiversity Science, Department of Biology, McGill University, Montreal, QC H3A 0G4, Canada eDepartment of Biology, Concordia University, Montreal, QC, H4B 1R6, Canada; fDepartment of Environmental Sciences, University of South Africa, Florida campus, Florida 1710, South Africa gDepartment of Biology, McGill University, Montreal, QC H3A 0G4, Canada hAfrican Centre for DNA Barcoding, University of Johannesburg, PO Box 524, Auckland Park, Johannesburg 2006, South Africa *Corresponding author Email: [email protected] (B.H. Daru) Running head: Phylogenetic regionalization of seagrasses 1 Abstract While our knowledge of species distributions and diversity in the terrestrial biosphere has increased sharply over the last decades, we lack equivalent knowledge of the marine world. Here, we use the phylogenetic tree of seagrasses along with their global distributions and a metric of phylogenetic beta diversity to generate a phylogenetically-based delimitation of marine phytoregions (phyloregions). We then evaluate their evolutionary affinities and explore environmental correlates of phylogenetic turnover between them. We identified 11 phyloregions based on the clustering of phylogenetic beta diversity values. Most phyloregions can be classified as either temperate or tropical, and even geographically disjunct temperate regions can harbor closely related species assemblages.
    [Show full text]
  • Using Edna to Determine the Source of Organic Carbon in Seagrass
    Page 1 of 37 Limnology and Oceanography ambiguity. Identifying the sources of OC to the sediments of blue C ecosystems is crucial for building robust and accurate C budgets for these systems. Accepted Article This is the author manuscript accepted for publication and has undergone full peer review but has not been through the copyediting, typesetting, pagination and proofreading process, which may lead to differences between this version and the Version record. Please cite this article as doi:10.1002/lno.10499. This article is protected by copyright. All rights reserved. Limnology and Oceanography Page 2 of 37 Title of article: Using eDNA to determine the source of organic carbon in seagrass meadows Authors’ complete names and institutional affiliations: Ruth Reef 1,2,3*, Trisha B Atwood 1,4* , Jimena Samper-Villarreal 5,6, Maria Fernanda Adame 7, Eugenia Sampayo 1, Catherine E Lovelock 1 1) Global Change Institute, University of Queensland, St Lucia QLD 4072 Australia 2) Department of Geography, University of Cambridge, Downing Site, Cambridge CB2 3EN United Kingdom 3) School of Earth, Atmosphere and Environment, Monash University, Clayton VIC 3800 Australia 4) Department of Watershed Sciences and Ecology Center, Utah State University, Logan, Utah 84322-5210, USA 5) Marine Spatial Ecology Lab and ARC Centre of Excellence for Coral Reef Studies, University of Queensland, St Lucia Qld 4072, Australia. 6) Centro de Investigación en Ciencias del Mar y Limnología (CIMAR) & Escuela de Biología, Universidad de Costa Rica, San Pedro, 11501-2060 San José, Costa Rica 7) Australian Rivers Institute, Griffith University, Nathan QLD 4111 Australia * Both authors contributed equally to this work Accepted Article Corresponding author: Dr Ruth Reef, Cambridge Coastal Research Unit, The University of Cambridge, CB2 3EN, United Kingdom.
    [Show full text]
  • Natural Products of Marine Macroalgae from South Eastern Australia, with Emphasis on the Port Phillip Bay and Heads Regions of Victoria
    marine drugs Review Natural Products of Marine Macroalgae from South Eastern Australia, with Emphasis on the Port Phillip Bay and Heads Regions of Victoria James Lever 1 , Robert Brkljaˇca 1,2 , Gerald Kraft 3,4 and Sylvia Urban 1,* 1 School of Science (Applied Chemistry and Environmental Science), RMIT University, GPO Box 2476V Melbourne, VIC 3001, Australia; [email protected] (J.L.); [email protected] (R.B.) 2 Monash Biomedical Imaging, Monash University, Clayton, VIC 3168, Australia 3 School of Biosciences, University of Melbourne, Parkville, Victoria 3010, Australia; [email protected] 4 Tasmanian Herbarium, College Road, Sandy Bay, Tasmania 7015, Australia * Correspondence: [email protected] Received: 29 January 2020; Accepted: 26 February 2020; Published: 28 February 2020 Abstract: Marine macroalgae occurring in the south eastern region of Victoria, Australia, consisting of Port Phillip Bay and the heads entering the bay, is the focus of this review. This area is home to approximately 200 different species of macroalgae, representing the three major phyla of the green algae (Chlorophyta), brown algae (Ochrophyta) and the red algae (Rhodophyta), respectively. Over almost 50 years, the species of macroalgae associated and occurring within this area have resulted in the identification of a number of different types of secondary metabolites including terpenoids, sterols/steroids, phenolic acids, phenols, lipids/polyenes, pheromones, xanthophylls and phloroglucinols. Many of these compounds have subsequently displayed a variety of bioactivities. A systematic description of the compound classes and their associated bioactivities from marine macroalgae found within this region is presented. Keywords: marine macroalgae; bioactivity; secondary metabolites 1.
    [Show full text]
  • Evaluation of the Host Range of Hydrellia Lagarosiphon
    Host range tests of Hydrellia lagarosiphon a candidate agent for Lagarosiphon major in New Zealand: assessing the risk to non-target species in New Zealand Jan-Robert Baars (University College Dublin), Quentin Paynter (Landcare Research New Zealand) Materials and Methods Selection of test plants A test plant list for New Zealand (henceforth NZ) (Table 1) was compiled using the centrifugal phylogenetic method (Wapshere, 1974) with amendments, as suggested by Briese and Walker (2002) and Briese (2003). Recent development in phylogenetics for the Hydrocharitaceae and its relation to taxonomically similar plant families were obtained by consulting the Angiosperm Phylogeny Website (Stevens, 2001 onwards; Fig. 1). Figure 1 Phylogeny of the Alismatales obtained from the Angiosperm Phylogeny Website: (Stevens, 2001 onwards) The most recent checklist of native NZ plants (De Lange and Rolfe, 2010) was examined to identify the NZ plant species that are most closely-related to lagarosiphon in order to compile a list of native plants for inclusion in host-range testing. Given that the aquatic lifestyle is a highly specialised one, relying totally on taxonomic position without due consideration of habitat has the potential to result in unsuitable test plants being included in a test list. For example, arthropod herbivores that feed on lagarosiphon are adapted to being submerged in freshwater and we can be sure that the marine eelgrass Zostera muelleri (Zosteriaceae) cannot be a suitable host for an insect herbivore because no insects have followed seagrasses into the ocean (Ollerton and McCollin, 1998). Zostera muelleri was, therefore, excluded from host- range testing. Wolffia australiana was also excluded from host-range testing as the tiny (0.3-1 mm long) platelets are far too small to be at risk of supporting the development of a leaf- mining fly.
    [Show full text]
  • Highly Restricted Dispersal in Habitat-Forming Seaweed
    www.nature.com/scientificreports OPEN Highly restricted dispersal in habitat‑forming seaweed may impede natural recovery of disturbed populations Florentine Riquet1,2*, Christiane‑Arnilda De Kuyper3, Cécile Fauvelot1,2, Laura Airoldi4,5, Serge Planes6, Simonetta Fraschetti7,8,9, Vesna Mačić10, Nataliya Milchakova11, Luisa Mangialajo3,12 & Lorraine Bottin3,12 Cystoseira sensu lato (Class Phaeophyceae, Order Fucales, Family Sargassaceae) forests play a central role in marine Mediterranean ecosystems. Over the last decades, Cystoseira s.l. sufered from a severe loss as a result of multiple anthropogenic stressors. In particular, Gongolaria barbata has faced multiple human‑induced threats, and, despite its ecological importance in structuring rocky communities and hosting a large number of species, the natural recovery of G. barbata depleted populations is uncertain. Here, we used nine microsatellite loci specifcally developed for G. barbata to assess the genetic diversity of this species and its genetic connectivity among ffteen sites located in the Ionian, the Adriatic and the Black Seas. In line with strong and signifcant heterozygosity defciencies across loci, likely explained by Wahlund efect, high genetic structure was observed among the three seas (ENA corrected FST = 0.355, IC = [0.283, 0.440]), with an estimated dispersal distance per generation smaller than 600 m, both in the Adriatic and Black Sea. This strong genetic structure likely results from restricted gene fow driven by geographic distances and limited dispersal abilities, along with genetic drift within isolated populations. The presence of genetically disconnected populations at small spatial scales (< 10 km) has important implications for the identifcation of relevant conservation and management measures for G.
    [Show full text]
  • Natural History of the Coorong
    Natural History of the Coorong, Lower Lakes, and Murray Mouth Region (yarluwar-ruwe) This book is available as a free fully searchable ebook from www.adelaide.edu.au/press Occasional publications of the Royal Society of South Australia Inc. Ideas & Endeavours: a History of the Natural Sciences in South Australia, published 1986. Natural History of the Adelaide Region, published 1976, reprinted 1988. Natural History of Eyre Peninsula, published 1985. Natural History of the Flinders Ranges, published 1996. Natural History of Kangaroo Island, second edition, published 2002. Natural History of the North East Deserts, published 1990. Natural History of the South East, published 1983, reprinted 1995. Natural History of Gulf St Vincent, published 2008. Natural History of Riverland and Murraylands, published 2009. Natural History of Spencer Gulf, published 2014. Natural History of the Coorong, Lower Lakes, and Murray Mouth Region (yarluwar-ruwe) Editors Luke Mosley, Qifeng Ye, Scoresby Shepherd, Steve Hemming, Rob Fitzpatrick Royal Society of South Australia Inc. Published in Adelaide by University of Adelaide Press Barr Smith Library The University of Adelaide South Australia 5005 [email protected] www.adelaide.edu.au/press on behalf of the Royal Society of South Australia Inc. © 2018 Royal Society of South Australia. This work is licenced under the Creative Commons Attribution-NonCommercial- NoDerivatives 4.0 International (CC BY-NC-ND 4.0) License. To view a copy of this licence, visit http://creativecommons.org/licenses/by-nc-nd/4.0 or send a letter to Creative Commons, 444 Castro Street, Suite 900, Mountain View, California, 94041, USA. This licence allows for the copying, distribution, display and performance of this work for non-commercial purposes providing the work is clearly attributed to the copyright holders.
    [Show full text]
  • ASBS Newsletter I Gave an Overview of Outside Our Sector), and of the Importance and Taxonomy Australia and Its Role and Governance
    Newsletter No. 177 December 2018 Price: $5.00 AUSTRALASIAN SYSTEMATIC BOTANY SOCIETY INCORPORATED Council President Vice President Darren Crayn Daniel Murphy Australian Tropical Herbarium (CNS) Royal Botanic Gardens Victoria James Cook University, Cairns Campus Birdwood Avenue PO Box 6811, Cairns Qld 4870 Melbourne, Vic. 3004 Australia Australia Tel: (+617)/(07) 4232 1859 Tel: (+613)/(03) 9252 2377 Email: [email protected] Email: [email protected] Secretary Treasurer Jennifer Tate Matt Renner Institute of Fundamental Sciences Royal Botanic Garden Sydney Massey University Mrs Macquaries Road Private Bag 11222, Palmerston North 4442 Sydney NSW 2000 New Zealand Australia Tel: (+646)/(6) 356- 099 ext. 84718 Tel: (+61)/(0) 415 343 508 Email: [email protected] Email: [email protected] Councillor Councillor Ryonen Butcher Heidi Meudt Western Australian Herbarium Museum of New Zealand Te Papa Tongarewa Locked Bag 104 PO Box 467, Cable St Bentley Delivery Centre WA 6983 Wellington 6140, New Zealand Australia Tel: (+644)/(4) 381 7127 Tel: (+618)/(08) 9219 9136 Email: [email protected] Email: [email protected] Other constitutional bodies Hansjörg Eichler Research Committee Affiliate Society David Glenny Papua New Guinea Botanical Society Sarah Mathews Heidi Meudt Joanne Birch Advisory Standing Committees Katharina Nargar Financial Murray Henwood Patrick Brownsey Chair: Dan Murphy, Vice President, ex officio David Cantrill Grant application closing dates Bob Hill Hansjörg Eichler Research Fund: th th Ad
    [Show full text]