Science Update an (Un)Common Murre Mortality Event
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Galveston, Texas
Galveston, Texas 1 TENTATIVE ITINERARY Participants may arrive at beach house as early as 8am Beach geology, history, and seawall discussions/walkabout Drive to Galveston Island State Park, Pier 21 and Strand, Apffel Park, and Seawolf Park Participants choice! Check-out of beach house by 11am Activities may continue after check-out 2 GEOLOGIC POINTS OF INTEREST Barrier island formation, shoreface, swash zone, beach face, wrack line, berm, sand dunes, seawall construction and history, sand composition, longshore current and littoral drift, wavelengths and rip currents, jetty construction, Town Mountain Granite geology Beach foreshore, backshore, dunes, lagoon and tidal flats, back bay, salt marsh wetlands, prairie, coves and bayous, Pelican Island, USS Cavalla and USS Stewart, oil and gas drilling and production exhibits, 1877 tall ship ELISSA Bishop’s Palace, historic homes, Pleasure Pier, Tremont Hotel, Galveston Railroad Museum, Galveston’s Own Farmers Market, ArtWalk 3 TABLE OF CONTENTS • Barrier Island System Maps • Jetty/Breakwater • Formation of Galveston Island • Riprap • Barrier Island Diagrams • Town Mountain Granite (Galveston) • Coastal Dunes • Source of Beach and River Sands • Lower Shoreface • Sand Management • Middle Shoreface • Upper Shoreface • Foreshore • Prairie • Backshore • Salt Marsh Wetlands • Dunes • Lagoon and Tidal Flats • Pelican Island • Seawolf Park • Swash Zone • USS Stewart (DE-238) • Beach Face • USS Cavalla (SS-244) • Wrack Line • Berm • Longshore Current • 1877 Tall Ship ELISSA • Littoral Zone • Overview -
(J3+5Q I-’ /Fq.057 I I SENSITIVITY of COASTAL ENVIRONMENTS and WILDLIFE to SPILLED OIL ALAS KA - SHELIKOF STRAIT REGION
i (J3+5q i-’ /fq.057 I I SENSITIVITY OF COASTAL ENVIRONMENTS AND WILDLIFE TO SPILLED OIL ALAS KA - SHELIKOF STRAIT REGION - Daniel D. Domeracki, Larry C. Thebeau, Charles D. Getter, James L. Sadd, and Christopher H. Ruby Research Planning Institute, Inc. Miles O. Hayes, President 925 Gervais Street Columbia, South Carolina 29201 - with contributions from - Dave Maiero Science Applications, Inc. and Dennis Lees - Dames and Moore PREPARED FOR: National Oceanic and Atmospheric Administration Outer Continental Shelf Environmental Assessment Program Juneau, Alaska RPI/R/81/2/10-4 Contract No. NA80RACO0154 February 1981 .i i . i ~hou~d read: 11; Caption !s Page 26, Figure four distinct biO1~~~cal rocky shore show~ng algae 2oner and P Exposed (1) barnacle (Balanus glandula) zone, zones: (3) -and ~~~e. blue mussel zone, ~ar-OSUsJ (4) barnacle ~B_ - . 27 -.--d. 29 ..-.A =~na beaches . 31 fixposed tidal flats (low biomass) . 33 Mixed sand and gravel beaches . 35 Gravel beaches . 37 Exposed tidal flats (moderate biomass) . 39 Sheltered rocky shores . ...*.. 41 Sheltered tidal flats . 43 Marshes ● =*...*. 45 Critical Species and Habitats . 47 Marine Mammals . ...*. 48 Coastal Marine Birds. 50 Finish . ...*.. 54 Shellfish . ...**.. ● *...... ...*.. ..* 56 Critical Intertidal Habitats . 58 Salt Marshes . 58 Sheltered Tidal Flats. 59 Sheltered Rocky Shores . 59 Critical Subtidal Habitats . 60 Nearshore Subtidal Habitats . ...*.. 60 Seagrass Beds . ...* ● . 62 Kelp Beds ● . ...**. ● .*...*. ...* . 63 ● . TABLE OF CONTENTS (continued) PAGE Discussion of Habitats with Variable to Slight Sensitivity. ...*..... 65 Introduction . 65 Exposed Rocky Shores. 65 Beaches . ● . 66 Exposed Tidal Flats.. 67 Areas of Socioeconomic Importance . 68 Mining Claims . 68 Private Property ● . 69 Public Property . ...*.. 69 Archaeological Sites. -
|||GET||| Apocalyptic Literature a Reader 1St Edition
APOCALYPTIC LITERATURE A READER 1ST EDITION DOWNLOAD FREE Mitchell G Reddish | 9781565632103 | | | | | Apocalyptic literature Just a moment while we sign you in to your Goodreads account. Create a Want Tell us what you're looking for and once a match is found, we'll inform you by e-mail. Sign in or create an account. Mitchell G. Early Old Testament prophecy taught the need of personal and national righteousness, and foretold the ultimate blessedness of the righteous nation on the present earth. Published by Abingdon Press. About this Item: Abingdon, This article is about the genre of religious writings dealing with revelation. Extinction Extinction event Holocene extinction Human extinction List of extinction events Genetic erosion Genetic pollution. Chassidei Ashkenaz. The descriptions not only tell of the end Apocalyptic Literature A Reader 1st edition, but also describe both past and present events and their significance, often in heavily coded Apocalyptic Literature A Reader 1st edition. The Similitudes of Enoch. As per university guidelines, more that six absences may Apocalyptic Literature A Reader 1st edition in your withdrawal from the course. Unread book in perfect condition. Be the first to ask a question about Apocalyptic Literature. Whereas prophecy had to deal with governments of other nations, apocalyptic writings Apocalyptic Literature A Reader 1st edition at a time when Israel had been subject for generations to the sway of one or other of the great world-powers. Teddi Pinson rated it really liked it Oct 26, About this Item: Hendrickson, Peabody, Ma, Condition: Acceptable. Leah marked it as to-read Apr 20, Michael Paul Cartledge added it Jan 30, Alien invasion Apocalyptic and post-apocalyptic fiction List of apocalyptic and post-apocalyptic fiction List of apocalyptic films Climate fiction Disaster films List of disaster films List of fictional doomsday devices Zombie apocalypse Zombie. -
Sea Urchin Diadema Africanum Mass Mortality in the Subtropical Eastern Atlantic: Role of Waterborne Bacteria in a Warming Ocean
Vol. 506: 1–14, 2014 MARINE ECOLOGY PROGRESS SERIES Published June 23 doi: 10.3354/meps10829 Mar Ecol Prog Ser FREEREE FEATURE ARTICLE ACCESSCCESS Sea urchin Diadema africanum mass mortality in the subtropical eastern Atlantic: role of waterborne bacteria in a warming ocean S. Clemente1,*, J. Lorenzo-Morales2, J. C. Mendoza1, C. López1, C. Sangil3, F. Alves4, M. Kaufmann4,5,6, J. C. Hernández1 1Biodiversidad, Ecología Marina y Conservación, Departamento de Biología Animal (Ciencias Marinas), Facultad de Biología, Universidad de La Laguna, Avda. Astrofísico Francisco Sánchez s/n, 38206 La Laguna, Tenerife, Canary Islands, Spain 2University Institute of Tropical Diseases and Public Health of the Canary Islands, Universidad de La Laguna, Avda. Astrofísico Francisco Sánchez s/n, 38203 La Laguna, Tenerife, Canary Islands, Spain 3Botánica Marina, Departamento de Biología Vegetal, Universidad de La Laguna, 38071 La Laguna, Tenerife, Canary Islands, Spain 4CIIMAR-Madeira (Interdisciplinary Centre of Marine and Environmental Research of Madeira), Edifício Madeira Tecnopolo, Caminho da Penteada, 9020-105 Funchal, Madeira, Portugal 5University of Madeira, Centre of Life Sciences, Marine Biology Station of Funchal, 9000-107 Funchal, Madeira, Portugal 6CIIMAR/CIMAR (Interdisciplinary Centre of Marine and Environmental Research), University of Porto, Rua dos Bragas 289, 4050-123 Porto, Portugal ABSTRACT: A widespread mass mortality event of the sea urchin Diadema africanum was detected in the subtropical eastern Atlantic, extending from Madeira to the Canary Islands, covering a straight- line distance of >400 km. This is the first disease- related die-off of a diadematid documented in the eastern Atlantic Ocean. Diseased individuals showed deterioration of the epidermis and water-vascular system, resulting in epidermal necrosis and release of spines. -
Peer Review of the Scientific Findings in the U.S
SUMMARY REPORT Peer Review of the Scientific Findings in the U.S. Fish and Wildlife Service Eagle Fatality Model and its Application to Wind Energy Development Projects DIVISION OF MIGRATORY BIRDS REGION 6 OFFICE U.S. FISH AND WILDLIFE SERVICE March 14, 2013 Prepared for: U.S. Fish and Wildlife Service Region 6 Office Lake Plaza North 134 Union Boulevard Lakewood, Colorado 80228-1807 Prepared by: AMEC Environment & Infrastructure, Inc. 1819 Denver West Drive Suite 100 Golden, CO 80401 USFWS Order No. F13PB00058 AMEC Project No. 32106C001 TABLE OF CONTENTS Executive Summary .................................................................................................. 1 1.0 Background ........................................................................................................ 4 2.0 Peer Reviewer Approach ................................................................................... 5 2.1 Description of Individual Reviewer‟s Role ....................................................... 5 2.2 Model Development and Description .............................................................. 6 2.3 Thousand Turbine Project (TTP) .................................................................... 8 2.4 PWRC Power Turbine Model Methods and Outputs ...................................... 9 3.0 Summary of Peer Review Responses .............................................................. 9 3.1 General Model Review Questions ................................................................ 10 3.2 1000 Turbine Project Peer Review -
Finfish Mortalities in Scotland
1 Report Rep21st January 2016 Finfish Mortalities in Scotland Project Code: 3RP005-502 2 |Finfish Mortalities in Scotland Contents Executive Summary 5 1 Introduction 9 2 The Finfish Aquaculture Industry in Scotland 10 2.1 Industry Overview 10 2.2 Active Marine Farms 10 2.3 Active Freshwater Atlantic Salmon Farms 11 2.4 Active Rainbow Trout Farms 11 3 Fish Farm Mortalities in Scotland 12 3.1 Marine Farms 12 3.2 Freshwater Production and Mortalities 14 4 Review of the Potential Processing and Logistics Infrastructure in Scotland for Managing Fish Farm Waste 15 4.1 Processing Fish Farm Waste through Existing AD and IVC Facilities 15 4.2 Processing Fish Farm Waste through Rendering and Incineration Infrastructure 15 5 Stakeholder Engagement Results – Processing and Logistics Companies 16 5.1 Overview 16 5.2 Fish Farming Companies 16 5.3 Anaerobic Digestion (AD) Operators 18 5.4 In Vessel Composting (IVC) Operators 23 5.5 Rendering Companies 26 5.6 Incineration & Co-Incineration 28 5.7 Hauliers / Logistics Companies 31 6 Analysis of Processing and Logistics Infrastructure Data 33 6.1 Anaerobic Digestion and IVC 33 6.2 Rendering and Incineration 34 6.3 Collection Services which Can Undertake the Transfer of Fish Farm Waste to Processing Facilities in Scotland 35 7 Costs / Incomes Associated with Options for Managing Fish Farm Waste 36 7.1 Overview 36 7.2 Income Stream for Energy Production Using Fish Waste 36 7.3 Summary of Costs to Fish Farm Operators 37 8 Impact on Remote Landfills 39 8.1 Stakeholder Engagement Results 39 8.2 Analysis of Revenue -
Stefano Goffredo · Zvy Dubinsky Editors Its History and Present
CORE Metadata, citation and similar papers at core.ac.uk Provided by Almae Matris Studiorum Campus Stefano Go redo · Zvy Dubinsky Editors The Mediterranean Sea Its history and present challenges Bioconstructions in the Mediterranean: 2 5 Present and Future Petar Kružić Abstract In the Mediterranean Sea, most important habitat formers are bioconstructors. Bioconstructors provide habitats for a large variety of organisms and these organisms rely on bioconstructors as a source of food and shelter. Marine bioconstructors in temperate seas have been recognized to have a structural and functional role of marine biodiversity (as a habitat formers and ecosystem engineers), the same as coral reefs in tropical regions. Bioconstructors are ranging from coralligenous formations (formed usually by coralline algae, sponges, cnidarians, and bryozoans) to vermetid reefs, deep-sea white corals and oyster banks. Some habitats like coral banks formed by shallow-water coral Cladocora caespitosa od deep-water coral Lophelia pertusa , together with coralligenous buildups and maerl beds are of special interest for scientists and people involving with nature protection. Habitat degradation, destruction, fragmentation and loss are the most dramatic conse- quences of anthropogenic pressures on natural ecosystems and marine bioconstructors as a part of that. Under the present climate warming trend, together with marine acidifi cation, new mass mortality events may occur in the near future, possibly driving a major biodiver- sity crisis in the Mediterranean Sea, -
Detrimental Effects of Ocean Acidification on the Economically
Received Date : 25-Jan-2013 Revised Date : 25-Jan-2013 Accepted Date : 29-Jan-2013 Article type : Primary Research Articles Detrimental effects of Ocean Acidification on the economically important Mediterranean red coral (Corallium rubrum) Running title: Ocean Acidification Corallium rubrum 12Bramanti L., 2Movilla J., 3Guron M., 2Calvo E., 5Gori A., 2Dominguez-Carrió C., 2Grinyó J., 2Lopez-Sanz A., 2Martinez-Quintana A., 24Pelejero C., 36Ziveri, P., 3Rossi S. Article 1California State University Northridge. 18111 Nordhoff st. 91330 Northridge, CA, USA 2Institut de Ciències del Mar, ICM-CSIC, Passeig Marítim de la Barceloneta 37-49, 08003, Barcelona, Spain 3ICTA-UAB, UAB Campus Cn s/n Cerdanyola del Vallés 08193 Barcelona, Spain. 4Institució Catalana de Recerca i Estudis Avançats (ICREA), Barcelona, Spain 5Centre Scientifique de Monaco, Avenue Saint Martin 98000 Monaco, Principality of Monaco 6 Department of Earth Sciences - Earth and Climate, Faculty of Earth and Life Sciences, VU Universiteit Amsterdam de Boelelaan 1085, 1081HV Amsterdam, The Netherlands Corresponding author: Lorenzo Bramanti Tel: +1 818 4708903 e-mail: [email protected] Keywords: Mediterranean red coral; Metabolic effects of Ocean Acidification; Climate change; Economic impact of Ocean Acidification; Calcification; Biochemical balance. Type of paper: Primary Research Article This article has been accepted for publication and undergone full peer review but has not been through the copyediting, typesetting, pagination and proofreading process, which may Accepted lead to differences between this version and the Version of Record. Please cite this article as doi: 10.1111/gcb.12171 © 2013 Blackwell Publishing Ltd Abstract The mean predicted decrease of 0.3 to 0.4 pH units in the global surface ocean by the end of the century has prompted urgent research to assess the potential effects of ocean acidification on the marine environment, with strong emphasis on calcifying organisms. -
Environmental Anomalies, Energetic Reserves and Fatty Acid Modifications in Oysters Coincide with an Exceptional Mortality Event
Vol. 401: 129–146, 2010 MARINE ECOLOGY PROGRESS SERIES Published February 22 doi: 10.3354/meps08407 Mar Ecol Prog Ser Environmental anomalies, energetic reserves and fatty acid modifications in oysters coincide with an exceptional mortality event Fabrice Pernet1,*, Jean Barret1, Claire Marty 2, Jeanne Moal3, Patrik Le Gall1, Pierre Boudry3 1Laboratoire Environnement Ressources du Languedoc Roussillon, Ifremer, Bd. Jean Monnet, 34200 Sète, France 2Cépralmar, Stratégie Concept Bât. 1, 1300 Av. Albert Einstein, 34000 Montpellier, France 3UMR M100 Physiologie et Ecophysiologie des Mollusques Marins, Ifremer, Technopole de Brest-Iroise, 29280 Plouzané, France ABSTRACT: Mortality of oysters Crassostrea gigas occurred along the coasts of France during sum- mer 2008, causing a serious crisis in French oyster production. During spring to summer 2008, 5 groups of 1-yr old oysters of different origins and ploidy levels deployed in the Thau lagoon (France) were sampled for biometrical and biochemical analyses; environmental parameters were monitored in the same area. Mortality occurred in 2 episodes: 13 May to 10 June and 24 June to 9 July. Wild-collected oysters showed mortality sooner than other groups but total overall mortality was 85% in all groups. Mortality occurred when seawater temperature was >19°C during the repro- ductive season when energetic reserves of oysters were at their lowest. Energy reserve levels and mortality in oysters seemed to be independent of reproductive effort, and most likely reflected an unusual deficit in phytoplankton. The level of bacterial fatty acids in oysters increased markedly before the second mortality event, probably indicating an enhancement of the microbial loop or decomposition processes. At the same time, unsaturation of oyster fatty acids decreased, suggesting a diet change, acclimatization to increasing temperature or, most likely, oxidative damage due to an enhanced production of reactive oxygen species, which are often associated with stressful situations. -
Wave Template
BIOLOGICAL EFFECTS OF MECHANICAL BEACH RAKING IN THE UPPER INTERTIDAL ZONE ON PADRE ISLAND NATIONAL SEASHORE, TEXAS prepared for and funded by Padre Island National Seashore by Tannika K. Engelhard and Kim Withers CENTER FOR COASTAL STUDIES December 1997 TAMU-CC-9706-CCS Texas A&M University-Corpus Christi The Island University BIOLOGICAL EFFECTS OF MECHANICAL BEACH RAKING IN THE UPPER INTERTIDAL ZONE ON PADRE ISALND NATIONAL SEASHORE, TEXAS by Tannika K. Engelhard and Kim Withers Project Officer Kim Withers, Ph.D. Research Scientist Center for Coastal Studies Texas A&M University-Corpus Christi 6300 Ocean Drive Corpus Christi, Texas Prepared for Padre Island National Seashore National Park Service, Department of the Interior Resource Management Division 9405 South Padre Island Drive Corpus Christi, Texas Contract No. 1443PX749070058 December 1997 TAMU-CC-9706-CCS EXECUTIVE SUMMARY Natural and man-made debris are common components of the upper intertidal zone on Gulf of Mexico beaches. Stranded pelagic algae, primarily Sargassum spp. (Phaeophyta, Fucales) and driftwood constitutes the bulk of natural material deposited as beach wrack on Padre Island National Seashore (PINS) (Amos, 1993; Smith et al., 1995). In 1950, a band approximately 14 m wide and 0.3 m deep was reported lining the Texas coast for over 300 mi (Gunter, 1979). PINS employs mechanical raking as a public-use management practice for removal of beach wrack to improve the aesthetic and recreational quality of the beach for visitors. The potential for disturbance of biotic components due to mechanical raking has bee recognized by resource managers within the National Seashore system. Some national parks regulate the type of equipment, depth of penetration into the sand and tire pressure of machinery to minimize impact to the natural resources while others actively prohibit mechanical removal to allow materials to provide nutrients to the sand through decomposition. -
Mass Mortality in Northwestern Mediterranean Rocky Benthic Communities: Effects of the 2003 Heat Wave
Global Change Biology (2009) 15, 1090–1103, doi: 10.1111/j.1365-2486.2008.01823.x Mass mortality in Northwestern Mediterranean rocky benthic communities: effects of the 2003 heat wave J. GARRABOU*, w ,R.COMAz, N. BENSOUSSAN*,M.BALLY*,P.CHEVALDONNE´ *, M. CIGLIANO§, D. DIAZ} ,J.G.HARMELIN*,M.C.GAMBI§,D.K.KERSTINGk, J. B. LEDOUX*, C. LEJEUSNE*,C.LINARES*,C.MARSCHAL*,T.PE´ REZ*,M.RIBESw , J. C. ROMANO**, E. SERRANOz,N.TEIXIDOz,O.TORRENTS*, M. ZABALAww, F. ZUBERERzz and C . C E R R A N O § § *UMR 6540 – DIMAR CNRS/Universite´ de’ Aix-Marseille, Centre d’Oce´anologie de Marseille, Station Marine d’Endoume, rue Batterie des Lions, 13007 Marseille, France, wInstitut de Cie`ncies del Mar CSIC, Passeig Marı´tim de la Barceloneta 37-49, E-08003 Barcelona, Spain, zCentre d’Estudis Avanc¸ats de Blanes CEAB-CSIC, Acce´s Cala St. Francesc 14, 17300 Blanes, Girona, Spain, §Stazione Zoologica ‘Anton Dohrn’, Villa Comunale, 80121 Napoli, Italy, }Instituto Espan˜ol de Oceanografı´a, C/Moll de Ponent s/n, 07015 Palma de Mallorca, Spain, kReserva Marina de Las Islas Columbretes, SGPM-Tragsa, Castello´, Spain, **UMR-CNRS 6134, Centre Scientifique de Vignola, route des Sanguinaires, 20000 Ajaccio, France, wwDepartament d’Ecologia, Universitat de Barcelona, Avda. Diagonal 645, 08028 Barcelona, Spain, zzUMS 2196 Centre d’Oce´anologie de Marseille, Station Marine d’Endoume, rue Batterie des Lions, 13007 Marseille, France, §§Dipartimento per lo Studio del Territorio e delle sue Risorse, Universita` di Genova, C.so Europa 26, 16132 Genova, Italy Abstract Late in summer 2003, extensive mass mortality of at least 25 rocky benthic macro- invertebrate species (mainly gorgonians and sponges) was observed in the entire North- western (NW) Mediterranean region, affecting several thousand kilometers of coastline. -
Assessment of Hybrid Type Shore Erosion Control Projects in Maryland’S Chesapeake Bay Phases I & II
Assessment of Hybrid Type Shore Erosion Control Projects in Maryland’s Chesapeake Bay Phases I & II David G. Burke Burke Environmental Associates Annapolis, Maryland Evamaria W. Koch & J. Court Stevenson Horn Point Environmental Laboratory University of Maryland Center for Environmental Science PO Box 775 Cambridge, Maryland 21613 Final Report Submitted To: Chesapeake Bay Trust 60 West Street, Suite 405 Annapolis, MD 21401 March, 2005 Table of Contents Executive Summary ………………………………………………………4 Part I: Summary of Project Assessment Locations and Types …………..6 Part II: Procedures and Protocols …………………………………………11 Part III: Site By Site Evaluation and Summary of Collected ……………..13 Data and Observations …………………………………………...13 Section A: Evaluation of Physical Parameters ………………..13 Section B: Biological and Water Quality Effectiveness Assessment ……………………………………….41 Section C: Summary Statement of Physical/Biological Effectiveness & Overall Conclusions ………….....66 Tables Table 1A. Project Locations – Phase I …………………………………..9 Table 1B. Project Locations – Phase II …………………………………..10 Table 2. Site Soil Characteristics …………………………………………12 Table 3. Fetch, Bank, and Project Types …………………………………13 Table 4A. Site Project Designs Phase I ………… ……………….............28 Table 4B. Site Project Designs Phase II ………… ………………............29 Table 5. Phase I Sites: Marsh “Break” Changes ..………………………...31 Table 6. Phase I Sites: Groin Elevations …………..……………………...35 Table 7. Phase I Sites: Sill Elevations ……………………………………...36 Table 8A. Phase II Sites: Sill Elevation, Marsh Slope and Erosion Data …37 Table 8B. Erosion Control Project Selection Criteria …….……..………..41 Table 9. Water column light characteristics and requirements at eastern shore sites ………………………………………………62 Table 10. Water Column Light Characteristics and Requirements at western shore sites ……………………………………………65 Figures Figure 1A. Significant Wave Height at DNR Sites ……….………………15 Figure 1B. Significant Wave Height at CBT Sites ……..…………………15 Figure 2A.