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High CO2 Reduces the Settlement of a Spawning Coral on Three Common Species of Crustose Coralline Algae
Vol. 475: 93–99, 2013 MARINE ECOLOGY PROGRESS SERIES Published February 14 doi: 10.3354/meps10096 Mar Ecol Prog Ser High CO2 reduces the settlement of a spawning coral on three common species of crustose coralline algae Christopher Doropoulos1,2,*, Guillermo Diaz-Pulido2,3 1School of Biological Sciences, The University of Queensland, St Lucia, Queensland 4072, Australia 2Australian Research Council Centre of Excellence for Coral Reef Studies, Queensland 4072, Australia 3School of Environment and Australian Rivers Institute, Griffith University, Nathan, Queensland 4111, Australia ABSTRACT: Concern about the impacts of ocean acidification (OA) on ecosystem function has prompted many studies to focus on larval recruitment, demonstrating declines in settlement and early growth at elevated CO2 concentrations. Since larval settlement is often driven by particular cues governed by crustose coralline algae (CCA), it is important to determine whether OA reduces larval recruitment with specific CCA and the generality of any effects. We tested the effect of elevated CO2 on the survival and settlement of larvae from the common spawning coral Acropora selago with 3 ecologically important species of CCA, Porolithon onkodes, Sporolithon sp., and Titanoderma sp. After 3 d in no-choice laboratory assays at 447, 705, and 1214 µatm pCO2, the rates of coral settlement declined as pCO2 increased with all CCA taxa. The magnitude of the effect was highest with Titanoderma sp., decreasing by 87% from the ambient to highest CO2 treatment. In general, there were high rates of larval mortality, which were greater with the P. onkodes and Sporolithon sp. treatments (~80%) compared to the Titanoderma sp. treatment (65%). -
Supplementary Material
Supplementary Material SM1. Post-Processing of Images for Automated Classification Imagery was collected without artificial light and using a fisheye lens to maximise light capture, therefore each image needed to be processed prior annotation in order to balance colour and to minimise the non-linear distortion introduced by the fisheye lens (Figure S1). Initially, colour balance and lenses distortion correction were manually applied on the raw images using Photoshop (Adobe Systems, California, USA). However, in order to optimize the manual post-processing time of thousands of images, more recent images from the Indian Ocean and Pacific Ocean were post- processed using compressed images (jpeg format) and an automatic batch processing in Photoshop and ImageMagick, the latter an open-source software for image processing (www.imagemagick.org). In view of this, the performance of the automated image annotation on images without colour balance was contrasted against images colour balanced using manual post-processing (on raw images) and the automatic batch processing (on jpeg images). For this evaluation, the error metric described in the main text (Materials and Methods) was applied to the images from following regions: the Maldives and the Great Barrier Reef (Figures S2 and S3). We found that the colour balance applied regardless the type of processing (manual vs automatic) had an important beneficial effect on the performance of the automated image annotation as errors were reduced for critical labels in both regions (e.g., Algae labels; Figures S2 and S3). Importantly, no major differences in the performance of the automated annotations were observed between manual and automated adjustments for colour balance. -
Ecology of Crustose Coralline Algae; Interactions with Scleractinian Corals and Responses to Environmental Conditions
Ecology of Crustose Coralline Algae; Interactions with Scleractinian Corals and Responses to Environmental Conditions Thesis submitted by Lindsay Mortan Harrington Bsc (California) in August 2004 For the Degree of Doctor of Philosophy In the School of Marine Biology and Aquaculture at James Cook University Statement of Contributions by Others I gratefully acknowledge the support of an International Postgraduate Research Scholarship (IPRS) Award from the James Cook University (JCU). I would like to extend my gratitude to the Cooperative Research Centre for the Great Barrier Reef World Heritage Area (CRC Reef), and the Australian Institute of Marine Science (AIMS) for funding this research. Some of the work I carried out for my PhD was collaborative, jointly published and/or done with technical, theoretical, statistical, editorial or physical assistance of others. I fully acknowledge the contributions by others as outlined below and detailed in the acknowledgements. To the best of my knowledge, all other work was done and written independently. Chapter 2 Dr. Glenn De'ath provided statistical assistance. Dr. Katharina Fabricius and Dr. Robert Steneck contributed to the intellectual and editorial work. Chapter 3 This chapter contains research that is part of a jointly published paper. Geoff Eaglesham conducted water analysis and characterization. Sediment analysis and characterization was carried out by Miriam Weber (Diplom thesis, 2003). Both Dr. Katharina Fabricius and Dr. Andrew Negri contributed to the intellectual, written and editorial work (see Appendix one, publication No. 2). Chapter 4 This chapter contains research that is part of a collaborative effort (see Appendix one, publication No. 3). Tiles were deployed by myself (inshore reefs GBR), Emre Turak (offshore reefs GBR) and Robert Steneck (reefs in the Caribbean). -
Shoeburyness Coastal Management Scheme Non- Technical Study
Shoeburyness Coastal Management Scheme Non- Technical Study Southend-on-Sea Borough Council This document is issued for the party which commissioned it and for specific purposes connected with the above-captioned project only. It should not be relied upon by any other party or used for any other purpose. We accept no responsibility for the consequences of this document being relied upon by any other party, or being used for any other purpose, or containing any error or omission which is due to an error or omission in data supplied to us by other parties. This document contains confidential information and proprietary intellectual property. It should not be shown to other parties without consent from us and from the party which commissioned it. The consultant has followed accepted procedure in providing the services but given the residual risk associated with any prediction and the variability which can be experienced in flood conditions, the consultant takes no liability for and gives no warranty against actual flooding of any property (client’s or third party) or the consequences of flooding in relation to the performance of the service. This report has been prepared for the purposes of informing the Shoeburyness Flood and Erosion Risk Management Scheme only. Shoeburyness Coastal Management Scheme 2 Contents Introduction 4 Aim of Document 4 Shoeburyness Coastal Management Scheme Area 5 The Need for Action 6 Key Issues for the Frontage 6 Section 1: Thorpe Bay Yacht Club to the groyne between the beachs huts on the beach and those on the promenade 6 Section 2: The groyne between the beach and those on the promenade to the H.M.Coastguard 6 Section 3: HM.Coastguard Station to World War 2 Quick Fire Battery 6 Flood and Erosion Risk 7 Flood Risk 7 Erosion Risk 7 Current Risks 7 Managing Impacts on the Environment 8 Designated Areas 8 Coastal Squeeze 8 Environmental Report 8 Appraisal Process 9 Task 1: Long List of Options 10 Task 2: Develop the Short List of Options 10 1. -
Coral Reef Algae
Coral Reef Algae Peggy Fong and Valerie J. Paul Abstract Benthic macroalgae, or “seaweeds,” are key mem- 1 Importance of Coral Reef Algae bers of coral reef communities that provide vital ecological functions such as stabilization of reef structure, production Coral reefs are one of the most diverse and productive eco- of tropical sands, nutrient retention and recycling, primary systems on the planet, forming heterogeneous habitats that production, and trophic support. Macroalgae of an astonish- serve as important sources of primary production within ing range of diversity, abundance, and morphological form provide these equally diverse ecological functions. Marine tropical marine environments (Odum and Odum 1955; macroalgae are a functional rather than phylogenetic group Connell 1978). Coral reefs are located along the coastlines of comprised of members from two Kingdoms and at least over 100 countries and provide a variety of ecosystem goods four major Phyla. Structurally, coral reef macroalgae range and services. Reefs serve as a major food source for many from simple chains of prokaryotic cells to upright vine-like developing nations, provide barriers to high wave action that rockweeds with complex internal structures analogous to buffer coastlines and beaches from erosion, and supply an vascular plants. There is abundant evidence that the his- important revenue base for local economies through fishing torical state of coral reef algal communities was dominance and recreational activities (Odgen 1997). by encrusting and turf-forming macroalgae, yet over the Benthic algae are key members of coral reef communities last few decades upright and more fleshy macroalgae have (Fig. 1) that provide vital ecological functions such as stabili- proliferated across all areas and zones of reefs with increas- zation of reef structure, production of tropical sands, nutrient ing frequency and abundance. -
Pleistocene Interglacial Sea-Levels on the Island of Alderney, Channel
Read at the Annual Conference of the Ussher Society, January 1997 PLEISTOCENE INTERGLACIAL SEA-LEVELS ON THE ISLAND OF ALDERNEY, CHANNEL ISLANDS H.C.L. JAMES James, H.C.L. 1997. Pleistocene interglacial sea-levels on the island of Alderney, Channel Islands. Proceedings of the Ussher Society, 9, 173-176. Brief references to raised beaches and associated phenomena on Alderney are reviewed in a historical context. More recent surveys by officers of the Institute of Geological Sciences demonstrated a series of raised beaches on Alderney within the context of the Channel Islands. This paper includes recently discovered sections which have been surveyed laterally and altitudinally. At least two distinct former sea-levels have been identified. H.C.L. James, Department of Science and Technology Education, The University of Reading, Bulmershe Court, Earley, Reading, Berkshire. RG6 1HY. BACKGROUND The earliest reference to raised beaches in Alderney appears in a Geological report to the Guernsey Society in 1894 (De la Mare, 1895). This was followed by Mourant's classic descriptions of evidence for former sea-levels in the Channel Islands (1933) including Alderney. Elhai (1963), using numerous published reports from the main Channel Islands' Societies, incorporated further descriptions of the Quaternary deposits within a broader consideration of the adjoining Normandy coast. More comprehensive recent reports on Pleistocene deposits on the island of Alderney appeared in Keen (1978). James (1989, 1990) added further sites and descriptions of low level raised beaches and suggested geochronological links with those of south-west England. RECENT WORK Keen's report for the Institute of Geological Sciences (1978) largely contained brief accounts of the location of raised beaches on Alderney within the context of his proposed three groups according to their height range (Figure 1) based on earlier work by Mourant (1933) and Zeuner (1959). -
Settlement Behavior of Acropora Palmata Planulae: Effects of Biofilm Age and Crustose Coralline Algal Cover
Proceedings of the 11th International Coral Reef Symposium, Ft. Lauderdale, Florida, 7-11 July 2008 Session number 24 Settlement behavior of Acropora palmata planulae: Effects of biofilm age and crustose coralline algal cover P.M. Erwin, B. Song, A.M. Szmant UNC Wilmington, Center for Marine Science, 5600 Marvin K. Moss Ln, Wilmington, NC 28409, USA Abstract. The role of crustose coralline algae (CCA) and bacterial biofilms in the settlement induction of Acropora palmata larvae was tested with ceramic tiles conditioned in reef waters for different time periods. Larval settlement varied among tiles by conditioning time (P<0.001), with low settlement (11%) on unconditioned tiles and high settlement (72-87%) on tiles conditioned for 2, 8 and 9 weeks. Tile surface texture and orientation also affected settlement (P<0.001). Larvae of A. palmata preferred the undersides of tiles as conditioned in the field (78% of total settlement), compared to upper surfaces (8%) or Petri dish surfaces (14%). CCA cover increased with conditioning time (P<0.001) and differed by tile orientation (P<0.005), revealing a positive correlation between settlement and CCA cover on tile bottoms, but not tile tops. Terminal restriction fragment length polymorphism (T-RFLP) analysis of 16S rRNA genes revealed that biofilm age, tile surface and tile orientation affected microbial community structure. Further, biofilms that induced settlement were characterized by bacterial populations distinct from non-inductive biofilm communities. Thus, we present additional evidence of the involvement of CCA and bacterial biofilm communities in the process of coral larval settlement, suggesting that complex interactions among multiple cues are involved in larval settlement choices. -
Target Substrata
TARGET SUBSTRATA OVERVIEW CORALS AND THEIR RELATIVES STONY HEXACORALS OTHER HEXACORALS OCTOCORALS HYDROZOANS Acropora Sea Anemones Soft Corals Fire Coral Non-Acropora Zoanthids Sea Fans Lace Coral Black Coral Blue Coral Hydroids Corallimorpharians Organ Pipe OTHER SUBSTRATA Sponge Macroalgae Dead Coral Rock Coralline Algae Dead Coral With Algae Rubble Algal Assemblage Turf Algae Sand Silt CORALS AND THEIR RELATIVES STONY CORALS ACROPORA Phylum Cnidaria | Class Anthozoa | Sub-Class Hexacorallia | Order Scleractinia (Hard Corals) | Family Acroporidae | Genus Acropora Acropora is one genus within the family of Acroporidae; Generally, the species are characterized by the presence of an axial (terminal) corallite (skeleton of an individual polyp) at the branch tips surrounded by radial corallites; The name Acropora is derived from the Greek “akron” which means summit. Acropora Branching Barefoot Conservation | TARGET SUBSTRATA | July 2016 1 Acropora Bottlebrush Acropora Digitate Acropora Tabulate Barefoot Conservation | TARGET SUBSTRATA | July 2016 2 Acropora Submassive Acropora Encrusting Non-Acropora Phylum Cnidaria | Class Anthozoa | Sub-Class Hexacorallia | Order Scleractinia (Hard Corals) | Family Acroporidae Coral Branching Barefoot Conservation | TARGET SUBSTRATA | July 2016 3 (continued) Coral Branching Coral Massive Barefoot Conservation | TARGET SUBSTRATA | July 2016 4 Coral Encrusting Coral Foliose Coral Submassive Barefoot Conservation | TARGET SUBSTRATA | July 2016 5 (continued) Coral Submassive Coral Mushroom Barefoot Conservation -
Period Summaries
Period summaries Palaeolithic – 450,000-12,000 BC Research over the past two decades has seen Sussex transformed from a backwater of the British Palaeolithic to an area of regional and global significance (Pope 2003). Analysis of raised beach deposits, terrestrial land-surfaces and periglacial gravels has indicated that they may preserve a record of climatic and environmental change over the past half a million years. Large areas of intact Pleistocene land-surface have been revealed by excavation that preserve traces of hominid tool production and a wide range of palaeo- environmental and faunal data. These discoveries underline the potential for the Palaeolithic period for the AONB, even though so far finds from this period are sparse (Fig 3). The raised beaches in Sussex are a series of wave-cut steps forming the coastal plain at the base of the South Downs. Isostatic uplift during the past 500,000 years has preserved ancient archaeological, environmental and palaeontological remains from marine erosion. As a result, the Sussex Coastal Plain is internationally important for the Palaeolithic period. To understand the relevance of this for the AONB, the wider context is outlined below. The Goodwood-Slindon Raised Beach is the highest of the series of Pleistocene marine deposits at 40m above sea level. Its east-west course across the Sussex Coastal Plain and possibly continuing into Hampshire has been traced for over 20km between Arundel and Funtington. Mineral extraction around Chichester has exposed the Goodwood-Slindon Raised Beach in a number of places. Stone tools have been recovered from the deposits, some unrolled suggesting they were in situ and had not been redeposited by wave action. -
Survey of the Extent of Human-Induced Beach Erosion Problems in Tanzania
Survey of the extent of human-induced beach erosion problems in Tanzania Item Type Proceedings Paper Authors Nyandwi, N. Citation Richmond, MD and Francis, J. (Ed). Marine Sciences Development in Tanzania and Eastern Africa. Proceeding of the 20th Anniversary Conference. p.121-129 Download date 27/09/2021 01:38:04 Link to Item http://hdl.handle.net/1834/821 Survey of the extent of human-induced beach erosion problems in Tanzania N. Nyandwi Institute of Marine Sciences, University of Dar es Salaam P.O. Box 668 Zanzibar, Dar es Salaam, Tanzania ABSTRACT An assessment of the coastal erosion problems along selected stretches around the Zanzibar coastline as well as along the mainland coastline of Tanzania, indicated a significant contribution to the problem by human activities. During the study, 56 eroding beaches were examined to assess the extent of anthropogenic activities to the problem. Human-induced erosion was observed at nine sites. By interfering with natural processes, human activities either initiated erosion or enhanced its rate. The activities identified fall into three categories namely, removal of beach material, removal of the protection against wave battering and obstruction of sediment supply. The observed human-induced erosion has occurred as a negative effect resulting from poor understanding of the natural processes. It was found that sand extraction from the beach for road construction was taking place on Zanzibar because many thought that beach sand is more needed for the roads than it is for the stability of the beach itself. Similarly, mangroves are being cleared in front of newly constructed tourist hotels because the developers are mainly concerned with having a clear view to the sea and absence of mangrove leaf litter to improve the hotel site aesthetics. -
Management Plan for Antarctic Specially Protected Area No. 126 BYERS PENINSULA, LIVINGSTON ISLAND, SOUTH SHETLAND ISLANDS
Measure 4 (2016) Management Plan for Antarctic Specially Protected Area No. 126 BYERS PENINSULA, LIVINGSTON ISLAND, SOUTH SHETLAND ISLANDS Introduction The primary reason for the designation of Byers Peninsula (latitude 62°34'35" S, longitude 61°13'07" W), Livingston Island, South Shetland Islands, as an Antarctic Specially Protected Area (ASPA) is to protect the terrestrial and lacustrine habitats within the Area. Byers Peninsula was originally designated as Specially Protected Area (SPA) No. 10 through Recommendation IV-10 in 1966. This area included the ice-free ground west of the western margin of the permanent ice sheet on Livingston Island, below Rotch Dome, as well as Window Island about 500 m off the northwest coast and five small ice-free areas on the south coast immediately to the east of Byers Peninsula. Values protected under the original designation included the diversity of plant and animal life, many invertebrates, a substantial population of southern elephant seals (Mirounga leonina), small colonies of Antarctic fur seals (Arctocephalus gazella), and the outstanding scientific values associated with such a large variety of plants and animals within a relatively small area. Designation as an SPA was terminated through Recommendation VIII-2 and redesignation as a Site of Special Scientific Interest (SSSI) was made through Recommendation VIII-4 (1975, SSSI No. 6). The new designation as an SSSI more specifically sought to protect four smaller ice-free sites on the peninsula of Jurassic and Cretaceous sedimentary and fossiliferous strata, considered of outstanding scientific value for study of the former link between Antarctica and other southern continents. Following a proposal by Chile and the United Kingdom, the SSSI was subsequently extended through Recommendation XVI-5 (1991) to include boundaries similar to those of the original SPA: i.e. -
St. Eustatius GCRMN 2017 Report (PDF)
ST. EUSTATIUS Prepared by: FINAL REPORT Kimani Kitson-Walters PhD (pending) Data Monitoring Officer 2017 Ministry of Agriculture, Nature and Food Quality /Caribbean Netherlands Science Institute L. E. Saddlerweg No 5 Oranjestad St. Eustatius, Caribbean Netherlands Email: [email protected] Table of Contents List of Figures .......................................................................................................................................... 2 List of Tables ........................................................................................................................................... 2 SUMMARY ............................................................................................................................................... 3 1. INTRODUCTION ................................................................................................................................... 3 2. METHODS ............................................................................................................................................ 3 2.1 Abundance and biomass of reef fish taxa ..................................................................................... 4 2.2 Relative cover of reef-building organisms (corals) and their dominant competitors .................. 4 2.3 Health assessment of reef-building corals .................................................................................... 5 2.4 Recruitment of reef-building corals .............................................................................................