Coral Reef Algae
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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%). -
RED ALGAE · RHODOPHYTA Rhodophyta Are Cosmopolitan, Found from the Artic to the Tropics
RED ALGAE · RHODOPHYTA Rhodophyta are cosmopolitan, found from the artic to the tropics. Although they grow in both marine and fresh water, 98% of the 6,500 species of red algae are marine. Most of these species occur in the tropics and sub-tropics, though the greatest number of species is temperate. Along the California coast, the species of red algae far outnumber the species of green and brown algae. In temperate regions such as California, red algae are common in the intertidal zone. In the tropics, however, they are mostly subtidal, growing as epiphytes on seagrasses, within the crevices of rock and coral reefs, or occasionally on dead coral or sand. In some tropical waters, red algae can be found as deep as 200 meters. Because of their unique accessory pigments (phycobiliproteins), the red algae are able to harvest the blue light that reaches deeper waters. Red algae are important economically in many parts of the world. For example, in Japan, the cultivation of Pyropia is a multibillion-dollar industry, used for nori and other algal products. Rhodophyta also provide valuable “gums” or colloidal agents for industrial and food applications. Two extremely important phycocolloids are agar (and the derivative agarose) and carrageenan. The Rhodophyta are the only algae which have “pit plugs” between cells in multicellular thalli. Though their true function is debated, pit plugs are thought to provide stability to the thallus. Also, the red algae are unique in that they have no flagellated stages, which enhance reproduction in other algae. Instead, red algae has a complex life cycle, with three distinct stages. -
Red Algae (Bangia Atropurpurea) Ecological Risk Screening Summary
Red Algae (Bangia atropurpurea) Ecological Risk Screening Summary U.S. Fish & Wildlife Service, February 2014 Revised, March 2016, September 2017, October 2017 Web Version, 6/25/2018 1 Native Range and Status in the United States Native Range From NOAA and USGS (2016): “Bangia atropurpurea has a widespread amphi-Atlantic range, which includes the Atlantic coast of North America […]” Status in the United States From Mills et al. (1991): “This filamentous red alga native to the Atlantic Coast was observed in Lake Erie in 1964 (Lin and Blum 1977). After this sighting, records for Lake Ontario (Damann 1979), Lake Michigan (Weik 1977), Lake Simcoe (Jackson 1985) and Lake Huron (Sheath 1987) were reported. It has become a major species of the littoral flora of these lakes, generally occupying the littoral zone with Cladophora and Ulothrix (Blum 1982). Earliest records of this algae in the basin, however, go back to the 1940s when Smith and Moyle (1944) found the alga in Lake Superior tributaries. Matthews (1932) found the alga in Quaker Run in the Allegheny drainage basin. Smith and 1 Moyle’s records must have not resulted in spreading populations since the alga was not known in Lake Superior as of 1987. Kishler and Taft (1970) were the most recent workers to refer to the records of Smith and Moyle (1944) and Matthews (1932).” From NOAA and USGS (2016): “Established where recorded except in Lake Superior. The distribution in Lake Simcoe is limited (Jackson 1985).” From Kipp et al. (2017): “Bangia atropurpurea was first recorded from Lake Erie in 1964. During the 1960s–1980s, it was recorded from Lake Huron, Lake Michigan, Lake Ontario, and Lake Simcoe (part of the Lake Ontario drainage). -
Benthic Communities at Two Remote Pacific Coral Reefs: Effects of Reef
Benthic communities at two remote Pacific coral reefs: eVects of reef habitat, depth, and wave energy gradients on spatial patterns Gareth J. Williams1,7 , Jennifer E. Smith1,7 , Eric J. Conklin2, Jamison M. Gove3,4 , Enric Sala5,6 and Stuart A. Sandin1 1 Scripps Institution of Oceanography, University of California, San Diego, La Jolla, CA, USA 2 The Nature Conservancy, Honolulu, Hawaii, USA 3 Coral Reef Ecosystem Division, Pacific Islands Fisheries Science Center, USA 4 Joint Institute for Marine and Atmospheric Research, University of Hawaii at Manoa, Honolulu, Hawaii, USA 5 National Geographic Society, Washington, DC, USA 6 Centre d’Estudis Avanc¸ats de Blanes (CSIC), Blanes, Spain 7 These authors contributed equally to this work. ABSTRACT Kingman Reef and Palmyra Atoll in the central Pacific are among the most re- mote coral reefs on the planet. Here we describe spatial patterns in their benthic communities across reef habitats and depths, and consider these in the context of oceanographic gradients. Benthic communities at both locations were dominated by calcifying organisms (54–86% cover), namely hard corals (20–74%) and crustose coralline algae (CCA) (10–36%). While turf algae were relatively common at both locations (8–22%), larger fleshy macroalgae were virtually absent at Kingman (<1%) and rare at Palmyra (0.7–9.3%). Hard coral cover was higher, but with low diversity, in more sheltered habitats such as Palmyra’s backreef and Kingman’s patch reefs. Al- most exclusive dominance by slow-growing Porites on Kingman’s patch reefs provides indirect evidence of competitive exclusion, probably late in a successional sequence. -
Vieira C., O. Camacho, Z. Sun, S. Fredericq, F. Leliaert, C. Payri & O
Molecular Phylogenetics and Evolution 110 (2017) 81–92 Contents lists available at ScienceDirect Molecular Phylogenetics and Evolution journal homepage: www.elsevier.com/locate/ympev Historical biogeography of the highly diverse brown seaweed Lobophora (Dictyotales, Phaeophyceae) q ⇑ Christophe Vieira a,b,c, , Olga Camacho d, Zhongmin Sun e, Suzanne Fredericq d, Frederik Leliaert b,f, Claude Payri a, Olivier De Clerck b a ENTROPIE (IRD, UR, CNRS), LabEx-CORAIL, Institut de Recherche pour le Développement, B.P. A5, 98848 Nouméa Cedex, Nouvelle-Calédonie, France b Phycology Research Group and Center for Molecular Phylogenetics and Evolution, Ghent University, Gent B-9000, Belgium c Sorbonne Universités, UPMC Univ Paris 06, IFD, Paris F75252, France d Department of Biology, University of Louisiana at Lafayette, Lafayette, LA 70504-3602, USA e Institute of Oceanology, Chinese Academy of Sciences, Department of Marine Organism Taxonomy and Phylogeny, China f Botanic Garden Meise, 1860 Meise, Belgium article info abstract Article history: The tropical to warm-temperate marine brown macroalgal genus Lobophora (Dictyotales, Phaeophyceae) Received 8 November 2016 recently drew attention because of its striking regional diversity. In this study we reassess Lobophora glo- Revised 22 February 2017 bal species diversity, and species distributions, and explore how historical factors have shaped current Accepted 4 March 2017 diversity patterns. We applied a series of algorithmic species delineation techniques on a global mito- Available online 6 March -
In Situ Tagging and Tracking of Coral Reef Fishes from the Aquarius Undersea Laboratory
TECHNICAL NOTE In Situ Tagging and Tracking of Coral Reef Fishes from the Aquarius Undersea Laboratory AUTHORS ABSTRACT James Lindholm We surgically implanted coded-acoustic transmitters in a total of 46 coral reef fish Stellwagen Bank National Marine Sanctuary; during a saturation mission to the Aquarius Undersea Laboratory in August 2002. Current address: Pfleger Institute of Aquarius is located within the Conch Reef Research Only Area, a no-take marine re- Environmental Research serve in the northern Florida Keys National Marine Sanctuary. Over the course of 10 Sarah Fangman days, with daily bottom times of 7 hrs, saturation diving operations allowed us to col- Channel Islands National Marine Sanctuary lect, surgically tag, release, and subsequently track fishes entirely in situ. Fish were collected using baited traps deployed adjacent to the reef as well as nets manipulated Les Kaufman on the bottom by divers. Surgical implantation of acoustic transmitters was conducted Boston University Marine Program at a mobile surgical station that was moved to different sites across the reef. Each fish Steven Miller was revived from anesthetic and released as divers swam the fish about the reef. Short- National Undersea Research Center, term tracking of tagged fish was conducted by saturation divers, while long-term fish University of North Carolina at Wilmington movement was recorded by a series of acoustic receivers deployed on the seafloor. Though not designed as an explicit comparison with surface tagging operations, the benefits of working entirely in situ were apparent. INTRODUCTION he use of acoustic telemetry to track the movements of marine fishes is now a com- true with deepwater fishes that have air blad- fish with a damp towel. -
Algae & Marine Plants of Point Reyes
Algae & Marine Plants of Point Reyes Green Algae or Chlorophyta Genus/Species Common Name Acrosiphonia coalita Green rope, Tangled weed Blidingia minima Blidingia minima var. vexata Dwarf sea hair Bryopsis corticulans Cladophora columbiana Green tuft alga Codium fragile subsp. californicum Sea staghorn Codium setchellii Smooth spongy cushion, Green spongy cushion Trentepohlia aurea Ulva californica Ulva fenestrata Sea lettuce Ulva intestinalis Sea hair, Sea lettuce, Gutweed, Grass kelp Ulva linza Ulva taeniata Urospora sp. Brown Algae or Ochrophyta Genus/Species Common Name Alaria marginata Ribbon kelp, Winged kelp Analipus japonicus Fir branch seaweed, Sea fir Coilodesme californica Dactylosiphon bullosus Desmarestia herbacea Desmarestia latifrons Egregia menziesii Feather boa Fucus distichus Bladderwrack, Rockweed Haplogloia andersonii Anderson's gooey brown Laminaria setchellii Southern stiff-stiped kelp Laminaria sinclairii Leathesia marina Sea cauliflower Melanosiphon intestinalis Twisted sea tubes Nereocystis luetkeana Bull kelp, Bullwhip kelp, Bladder wrack, Edible kelp, Ribbon kelp Pelvetiopsis limitata Petalonia fascia False kelp Petrospongium rugosum Phaeostrophion irregulare Sand-scoured false kelp Pterygophora californica Woody-stemmed kelp, Stalked kelp, Walking kelp Ralfsia sp. Silvetia compressa Rockweed Stephanocystis osmundacea Page 1 of 4 Red Algae or Rhodophyta Genus/Species Common Name Ahnfeltia fastigiata Bushy Ahnfelt's seaweed Ahnfeltiopsis linearis Anisocladella pacifica Bangia sp. Bossiella dichotoma Bossiella -
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. -
BS Marine Biology Course Descriptions
UNIVERSITY OF TEXAS RIO GRANDE VALLEY BS Marine Biology Course Descriptions A – GENERAL EDUCATION CORE – 42 HOURS Students must fulfill the General Education Core requirements. The courses listed in this section satisfy both degree requirements and General Education core requirements. MATH 1343 Introduction to Biostatistics Topics include introduction to biostatistics; biological and health studies and designs; probability and statistical inferences; one- and two-sample inferences for means and proportions; one-way ANOVA and nonparametric procedures. Prerequisites: College Ready TSI status in Mathematics. OR MATH 1388 Honors Topics include introduction to biostatistics; biological and health studies and designs; probability and statistical inferences; one- and two-sample inferences for means and proportions; one-way ANOVA and nonparametric procedures. Prerequisites: College Ready TSI status in mathematics and admission to the honors program CHEM 1311 General Chemistry I Fundamentals of atomic structure, electronic structure and periodic table, nomenclature, the stoichiometry reactions, gas laws, thermochemistry, chemical bonding, and structure and geometry of molecules. Prerequisites: MATH 1314, MATH 1414, MATH 1342, MATH 1343, MATH 1388, MATH 2412, MATH 2413, or MATH 2487 with a grade of “C” or higher.” CHEM 1312 General Chemistry II This course presents the properties of liquids and solids, solutions-acid-base theory, chemical kinetics, equilibrium, chemical thermodynamics, electrochemistry, nuclear chemistry, and representative organic compounds. Prerequisites: CHEM 1311 PHIL 1366 Philosophy and History of Science and Technology This course is designed to use history and philosophy in the service of science and engineering education. It does this by examining a selection of notable episodes in the history of science and Techno-Science. -
Taxonomic Checklist of CITES Listed Coral Species Part II
CoP16 Doc. 43.1 (Rev. 1) Annex 5.2 (English only / Únicamente en inglés / Seulement en anglais) Taxonomic Checklist of CITES listed Coral Species Part II CORAL SPECIES AND SYNONYMS CURRENTLY RECOGNIZED IN THE UNEP‐WCMC DATABASE 1. Scleractinia families Family Name Accepted Name Species Author Nomenclature Reference Synonyms ACROPORIDAE Acropora abrolhosensis Veron, 1985 Veron (2000) Madrepora crassa Milne Edwards & Haime, 1860; ACROPORIDAE Acropora abrotanoides (Lamarck, 1816) Veron (2000) Madrepora abrotanoides Lamarck, 1816; Acropora mangarevensis Vaughan, 1906 ACROPORIDAE Acropora aculeus (Dana, 1846) Veron (2000) Madrepora aculeus Dana, 1846 Madrepora acuminata Verrill, 1864; Madrepora diffusa ACROPORIDAE Acropora acuminata (Verrill, 1864) Veron (2000) Verrill, 1864; Acropora diffusa (Verrill, 1864); Madrepora nigra Brook, 1892 ACROPORIDAE Acropora akajimensis Veron, 1990 Veron (2000) Madrepora coronata Brook, 1892; Madrepora ACROPORIDAE Acropora anthocercis (Brook, 1893) Veron (2000) anthocercis Brook, 1893 ACROPORIDAE Acropora arabensis Hodgson & Carpenter, 1995 Veron (2000) Madrepora aspera Dana, 1846; Acropora cribripora (Dana, 1846); Madrepora cribripora Dana, 1846; Acropora manni (Quelch, 1886); Madrepora manni ACROPORIDAE Acropora aspera (Dana, 1846) Veron (2000) Quelch, 1886; Acropora hebes (Dana, 1846); Madrepora hebes Dana, 1846; Acropora yaeyamaensis Eguchi & Shirai, 1977 ACROPORIDAE Acropora austera (Dana, 1846) Veron (2000) Madrepora austera Dana, 1846 ACROPORIDAE Acropora awi Wallace & Wolstenholme, 1998 Veron (2000) ACROPORIDAE Acropora azurea Veron & Wallace, 1984 Veron (2000) ACROPORIDAE Acropora batunai Wallace, 1997 Veron (2000) ACROPORIDAE Acropora bifurcata Nemenzo, 1971 Veron (2000) ACROPORIDAE Acropora branchi Riegl, 1995 Veron (2000) Madrepora brueggemanni Brook, 1891; Isopora ACROPORIDAE Acropora brueggemanni (Brook, 1891) Veron (2000) brueggemanni (Brook, 1891) ACROPORIDAE Acropora bushyensis Veron & Wallace, 1984 Veron (2000) Acropora fasciculare Latypov, 1992 ACROPORIDAE Acropora cardenae Wells, 1985 Veron (2000) CoP16 Doc. -
Aquarius Fact Sheet
Fact Sheet: 2019 Designer: Perry Submarine Builders (Florida) Construction: Victoria Machine Works (Texas); start: 1986 | complete: 1987 Estimated construction cost: $5.5M Operational Timeline: St. Croix Deployment: Deployment in Salt River Canyon, St. Croix: 1987 Owner: NOAA Operator: Farleigh Dickenson University Interim Period: Recovered: 1990 by the University of North Carolina Wilmington Refurbished: 1990-1993 at North Carolina State Ports, Wilmington, NC Owner: NOAA Operator: University of North Carolina Wilmington Florida Keys Deployment: Initial deployment on Conch Reef, Florida Keys: 1993 (baseplate deployed 1992) Recovered for refurbishment: 1996-1998 - Harbor Branch Oceanographic Institution, Ft. Pierce, FL Redeployment on Conch Reef, Florida Keys: 1998 – present Owner: NOAA: 1986-2014; Florida International University: 2014 – present Operator: FDU: 1987-1989; UNCW: 1990-2012; Florida International University: 2013 - present Aquarius Siting: Conch Reef, Florida Keys (Florida Keys National Marine Sanctuary): Distance From Islamorada shore base: 15.4 km (8.5 nm) Distance offshore: 9 km (5.4 nm) Hatch depth/storage depth: 14 m (46 fsw) 35 psi Depth of bottom directly below Aquarius: 18 m (60 fsw) (updated: 09.15.19) Habitat Specifications: Aquarius weight: 82-ton double-lock pressure vessel Baseplate weight: 120 tons Dimensions: 14-meters long by 3-meters in diameter (46 ft x 10 ft) Crew: 4 scientists and 2 technicians Amenities: kitchen facilities that include a microwave, instant hot water dispenser, refrigerator, sink, dining -
Exposure to Elevated Sea-Surface Temperatures Below the Bleaching Threshold Impairs Coral Recovery and Regeneration Following Injury
A peer-reviewed version of this preprint was published in PeerJ on 18 August 2017. View the peer-reviewed version (peerj.com/articles/3719), which is the preferred citable publication unless you specifically need to cite this preprint. Bonesso JL, Leggat W, Ainsworth TD. 2017. Exposure to elevated sea-surface temperatures below the bleaching threshold impairs coral recovery and regeneration following injury. PeerJ 5:e3719 https://doi.org/10.7717/peerj.3719 Exposure to elevated sea-surface temperatures below the bleaching threshold impairs coral recovery and regeneration following injury Joshua Louis Bonesso Corresp., 1 , William Leggat 1, 2 , Tracy Danielle Ainsworth 2 1 College of Public Health, Medical and Veterinary Sciences, James Cook University, Townsville, Australia 2 Centre of Excellence for Coral Reef Studies, James Cook University, Townsville, Australia Corresponding Author: Joshua Louis Bonesso Email address: [email protected] Elevated sea surface temperatures (SSTs) are linked to an increase in the frequency and severity of bleaching events due to temperatures exceeding corals’ upper thermal limits. The temperatures at which a breakdown of the coral-Symbiodinium endosymbiosis (coral bleaching) occurs are referred to as the upper thermal limits for the coral species. This breakdown of the endosymbiosis results in a reduction of corals’ nutritional uptake, growth, and tissue integrity. Periods of elevated sea surface temperature, thermal stress and coral bleaching are also linked to increased disease susceptibility and an increased frequency of storms which cause injury and physical damage to corals. Herein we aimed to determine the capacity of corals to regenerate and recover from injuries (removal of apical tips) sustained during periods of elevated sea surface temperatures which result in coral stress responses, but which do not result in coral bleaching (i.e.