Identification of Environmental Loss Indicators Due to Oil Tanker Failures
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Oil Pollution in the North Sea: the Impact of Governance Measures on Oil Pollution Over Several Decades
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by White Rose Research Online Hydrobiologia https://doi.org/10.1007/s10750-018-3559-2 NORTH SEA OPEN SCIENCE CONFERENCE Review Paper Oil pollution in the North Sea: the impact of governance measures on oil pollution over several decades Angela Carpenter Received: 4 April 2017 / Revised: 22 February 2018 / Accepted: 24 February 2018 Ó The Author(s) 2018. This article is an open access publication Abstract Oil pollution entering the marine environ- This paper illustrates that international cooperation ment has been an issue of concern for many decades. It can result in a reduction in marine pollution leading to can come from riverine or land-based sources, acci- a cleaner environment. dental and intentional discharges from ships, or as a by-product of offshore oil extraction. Growing aware- Keywords Oil pollution Á North Sea Á ness of the impact of oil pollution on the marine Environmental monitoring Á Environmental policy Á environment has led, since the late 1960s, to the Regional cooperation Á Monitoring and surveillance introduction of measures to reduce or eliminate pollution from shipping and the offshore oil industry. A framework for environmental protection of the North Sea has developed over many decades through Introduction international agreements, regional cooperation, and national measures, while education has also played an Oil pollution—petroleum hydrocarbons—can enter important role with modern-day sailors being given the marine environment from a wide range of sources due training to understand that dumping waste at sea is including transport (e.g. -
An Example from the Amoco Cadiz Oil Spill
THE IMPORTANCE OF USING APPROPRIATE EXPERIMENTAL DESIGNS IN OIL SPILL IMPACT STUDIES: AN EXAMPLE FROM THE AMOCO CADIZ OIL SPILL IMPACT ZONE Downloaded from http://meridian.allenpress.com/iosc/article-pdf/1987/1/503/2349658/2169-3358-1987-1-503.pdf by guest on 27 September 2021 Edward S. Gilfillan, David S. Page, Barbara Griffin, Sherry A. Hanson, Judith C. Foster Bowdoin College Marine Research Laboratory and Bowdoin College Hydrocarbon Research Center Brunswick, Maine 04011 ABSTRACT: On March 16, 1978, the tanker Amoco Cadiz ran factors as possible in a sampling program to look at oil spill effects. aground off the coast of North Brittany. Her cargo of 221,000 tons of When using non-specific stress responses, it is important to be sure light crude oil was released into the sea. More than 126 miles of coast- just which Stressors are producing any observed responses. Multi- line were oiled, including a number of oyster (Crassostrea gigas j grow- variate statistical methods appear to be useful in associating body ing establishments. The North Brittany coastline already was stressed burdens of multiple Stressors with observed physiological effects. by earlier additions of oil and metals. In a field study by Gilfillan et al.,6 it was shown, using multivariate In December 1979, 21 months after the oil spill, measurements of techniques, that in populations of Mytilus edulis from a moderately glucose-6-phosphate dehydrogenase activity, aspartate aminotransfer- polluted estuary the animals were responding to Cu, Cr, and Cd at the ase activity, and condition index were made in 14 populations of C. -
Crisis-Induced Learning and Issue Politicization in the Eu: the Braer, Sea Empress, Erika,Andprestige Oil Spill Disasters
doi: 10.1111/padm.12170 CRISIS-INDUCED LEARNING AND ISSUE POLITICIZATION IN THE EU: THE BRAER, SEA EMPRESS, ERIKA,ANDPRESTIGE OIL SPILL DISASTERS WOUT BROEKEMA This article explores the relation between issue politicization and crisis-induced learning by the EU. We performed a political claims analysis on the political response to the four major oil spill disasters that have occurred in European waters since 1993. Political claims that we observed in three arenas (mass media, national parliaments, and the European Parliament) were compared with recommen- dations in post-crisis evaluation reports and the EU’s legislative responses. For all three political arenas our findings indicate that politicization of issues either promotes or impedes crisis-induced EU learning, which points to the existence of determining intervening factors. EU legislation that is adopted in response to oil spill disasters appears to a large extent grounded in crisis evaluation reports. Characteristics of crisis evaluation reports, especially the degree of international focus, seem to offer a more plausible explanation for variance in crisis-induced learning outcomes than politi- cization. INTRODUCTION On 15 January 1996, the Liberian-registered oil tanker Sea Empress ran aground on the rocks at the entrance to Milford Haven, releasing 72,000 tonnes of oil into the sea in the following days. Only three years later, on 12 December 1999, a very similar accident occurred in the European Atlantic when the Maltese-registered tanker Erika sank due to rough weather conditions off the Brittany coast, causing an oil spill of 20,000 tonnes. Both accidents had a dramatic long-term environmental, social, and economical transboundary impact (EMSA 2004; Wene 2005). -
Guide to the American Petroleum Institute Photograph and Film Collection, 1860S-1980S
Guide to the American Petroleum Institute Photograph and Film Collection, 1860s-1980s NMAH.AC.0711 Bob Ageton (volunteer) and Kelly Gaberlavage (intern), August 2004 and May 2006; supervised by Alison L. Oswald, archivist. August 2004 and May 2006 Archives Center, National Museum of American History P.O. Box 37012 Suite 1100, MRC 601 Washington, D.C. 20013-7012 [email protected] http://americanhistory.si.edu/archives Table of Contents Collection Overview ........................................................................................................ 1 Administrative Information .............................................................................................. 1 Arrangement..................................................................................................................... 3 Biographical / Historical.................................................................................................... 2 Scope and Contents........................................................................................................ 2 Names and Subjects ...................................................................................................... 4 Container Listing ............................................................................................................. 6 Series 1: Historical Photographs, 1850s-1950s....................................................... 6 Series 2: Modern Photographs, 1960s-1980s........................................................ 75 Series 3: Miscellaneous -
Sediment Contaminant Surveillance in Milford Haven Waterway
Sediment contaminant surveillance in Milford Haven Waterway D. I. Little, B. Bullimore, Y. Galperin and W. J. Langston D. I. Little, Environmental Consultancy, Swavesey, Cambridge CB24 4RL, UK; e-mail: [email protected] B. Bullimore, Deep Green Seas, Marine Environmental Consultancy, Tiers Cross, Haverfordwest SA62 3DG, UK Y. Galperin, Environmental Geochemistry Consulting, Moorpark, California 93021, USA W. J. Langston, Marine Biological Association, Citadel Hill, Plymouth PL1 2PB, UK Abstract Sediment contaminants were monitored in Milford Haven Waterway (MHW) since 1978 (hydrocarbons) and 1982 (metals), with the aim of providing surveillance of environmental quality in one of the UK’s busiest oil and gas ports. This aim is particularly important during and after large-scale investment in liquefied natural gas (LNG) facilities. However, methods inevitably have changed over the years, compounding the difficulties of coordinating sampling and analytical programmes. After a review by the MHW Environmental Surveillance Group (MHWESG), sediment hydrocarbon chemistry was investigated in detail in 2010. Natural Resources Wales (NRW) contributed their MHW data for 2007 and 2012, collected to assess the condition of the Special Area of Conservation (SAC) designated under the European Union Habitats Directive. Datasets during 2007-2012 have thus been more comparable. The results showed conclusively that a MHW-wide peak in concentrations of sediment polycyclic aromatic hydrocarbons (PAHs), metals and other contaminants occurred in late 2007. This was corroborated by independent annual monitoring at one centrally-located station with peaks in early 2008 and 2011. The spatial and temporal patterns of recovery from the 2007 peak, shown by MHW- wide surveys in 2010 and 2012, indicate several probable causes of contaminant trends, as follows: atmospheric deposition, catchment runoff, sediment resuspension from dredging, and construction of two LNG terminals and a power station. -
Ultimate and Residual Strength Assessment of Ship Structures
CHALMERS UNIVERSITY OF TECHNOLOGY Gothenburg, Sweden www.chalmers.se LICENTIATE THESIS ARTJOMS KUZNECOVS U ltimate and Residual Strength Assessment of Ship Structures Ultimate and Residual Strength Assessment of Ship Structures ARTJOMS KUZNECOVS DEPARTMENT OF MECHANICS AND MARITIME SCIENCES CHALMERS UNIVERSITY OF TECHNOLOGY 2 020 Gothenburg, Sweden 2020 www.chalmers.se THESIS FOR THE DEGREE OF LICENTIATE OF ENGINEERING Ultimate and Residual Strength Assessment of Ship Structures ARTJOMS KUZNECOVS Department of Mechanics and Maritime Sciences CHALMERS UNIVERSITY OF TECHNOLOGY Gothenburg, Sweden 2020 Ultimate and Residual Strength Assessment of Ship Structures ARTJOMS KUZNECOVS © ARTJOMS KUZNECOVS, 2020 Report No 2020:07 Chalmers University of Technology Department of Mechanics and Maritime Sciences Division of Marine Technology SE-412 96, Gothenburg Sweden Telephone: + 46 (0)31-772 1000 Printed by Chalmers Reproservice Gothenburg, Sweden 2020 Ultimate and Residual Strength Assessment of Ship Structures ARTJOMS KUZNECOVS Chalmers University of Technology Department of Mechanics and Maritime Sciences Division of Marine Technology Abstract The prevention of ship structural failures and reduction of accident consequences contribute to increased safety at sea and reduced environmental impact. A need for reliable and efficient ship designs facilitates knowledge accumulation and the development of tools for the assessment of hull structural responses to acting loads. Important in this regard, ship design criteria are the ultimate and residual strengths of a hull that determine whether a ship may be safely operated in intact and accidentally damaged conditions. Thus, an accurate and reliable procedure for estimating a ship’s strength accounting for all actual foreseeable scenarios and reasonably practicable conditions is necessary. The main objective of this thesis is to develop a new precise and time-efficient methodology for the assessment of the ultimate and residual strength under vertical and biaxial loading conditions. -
States of Emergency
STATES OF EMERGENCY Technological Failures and Social Destabilization Patrick Lagadec Contents Introduction PART ONE Technical Breakdown, Crisis and Destabilization Framework of Reference 1. The weapons of crisis ........................................................................................ 11 1. An unusual event in a metastable context .......................................................... 12 2. Crisis dynamics................................................................................................... 21 2. Organizations with their backs to the wall...................................................... 23 1. Classic destabilization scenarios ......................................................................... 24 2. Slipping out of control ....................................................................................... 35 PART TWO Technological Crisis and the Actors Involved 3- In the thick of things ....................................................................................... 43 - Marc Becam ....................................................................................................... 45 The oil spill from the "Amoco Cadiz", March - May, 1978 - Richard Thornburgh........................................................................................... 55 Three Mile Island, March - April, 1979 - Douglas K. Burrows .......................................................................................... 66 The great Mississauga evacuation, November 10-16. 1979 - Péter-J.Hargitay .............................................................................................. -
An Environmental Restoration Programme 12 Years After: the HAVEN Wreck
Les journées d’information du CEDRE – 6 octobre 2003 Le Traitement des Epaves Potentiellement Polluantes An Environmental Restoration Programme 12 Years After: the HAVEN Wreck E. Amato ICRAM–Central institute for marine applied research Via di Casalotti 300, 00166 Rome, Italy [email protected] Synopsis The VLCC “HAVEN” accident is the major case of oil spill ever occurred in the Mediterranean Sea. On April 11th 1991, while the “HAVEN” was anchored in front of the port of Genoa, two violent explosions started a fire within the ship that was extinguished only 70 hours later when the Very Large Crude Carrier sunk. At the moment of the accident the ship was carrying 144.000 tons of “heavy Iranian crude oil”. A large quantity of burnt oil rapidly sank in form of bitumen, while the rest of the cargo was dispersed by the Ligurian-Provençal current and by the winds. 1 Les journées d’information du CEDRE – 6 octobre 2003 Le Traitement des Epaves Potentiellement Polluantes During the emergency phase operations began in order to contain the pollution. Two important decisions were taken: to tug the ship coastward and to allow the burning of the greatest part of the oil spilled at sea. The operations concerned the containment of the spilled oil, the collection of the oil both at sea and on shore and the performing of an environmental control and monitoring plan. Twelve years later a restoration programme is on the way mainly dealing with the tar residues laying on the seabed and with the oil products still contained in the wreck. -
The Oil Pollution Act of 1990: Reaction and Response
Volume 3 Issue 2 Article 2 1992 The Oil Pollution Act of 1990: Reaction and Response Michael P. Donaldson Follow this and additional works at: https://digitalcommons.law.villanova.edu/elj Part of the Environmental Law Commons Recommended Citation Michael P. Donaldson, The Oil Pollution Act of 1990: Reaction and Response, 3 Vill. Envtl. L.J. 283 (1992). Available at: https://digitalcommons.law.villanova.edu/elj/vol3/iss2/2 This Article is brought to you for free and open access by Villanova University Charles Widger School of Law Digital Repository. It has been accepted for inclusion in Villanova Environmental Law Journal by an authorized editor of Villanova University Charles Widger School of Law Digital Repository. Donaldson: The Oil Pollution Act of 1990: Reaction and Response 19921 THE OIL POLLUTION ACT OF 1990: REACTION AND RESPONSE MICHAEL P. DONALDSONt TABLE OF CONTENTS I. INTRODUCTION ....................................... 283 II. PRE-OPA OIL SPILL LIABILITY ..........................284 III. THE OIL POLLUTION ACT OF 1990 .................... 288 IV. PREVIOUSLY CONSIDERED APPROACHES ................ 301 A. International Liability and Compensation Conventions ..................................... 301 B. Approaches Suggested by Congress .............. 305 V. CONCERNS AND REACTIONS TO THE OIL POLLUTION ACT OF 1990 ............................................. 3 13 A. Reaction by Industry ............................ 313 B. International Reactions .......................... 317 VI. CONCLUSION ........................................ -
Dti Strategic Environmental Assessment Area 8 (Sea8)
DTI STRATEGIC ENVIRONMENTAL ASSESSMENT AREA 8 (SEA8) Contamination of Water and Sediments Compiled by: Carolyn Voisey Assisted by: Deborah Tyrrell Other Contributors: Steve Rowlatt1 1The Centre for Environment, Fisheries and Aquaculture Science (CEFAS), Burnham-on-Crouch Contract Number SEA678_CV_data8CB Final Report March 2004 SEA8 Contamination of Water and Sediments Acknowledgements In addition to the authors, many scientists and workers in the marine industry contributed references to the database and their contributions are gratefully acknowledged. Table of Contents Acknowledgements ....................................................................................i Table of Contents.......................................................................................i List of Appendices......................................................................................i List of Tables ..............................................................................................ii List of Figures.............................................................................................ii 1 Introduction..........................................................................................1 2 Description of the Study Area ............................................................2 2.1 Introduction.........................................................................................2 2.2 English Channel..................................................................................3 2.3 South-Western Approaches...............................................................3 -
Study on Effective Methods Foroil Products Cleaning
1 Plant Archives Vol. 19, Supplement 2, 2019 pp. 483-489 e-ISSN:2581-6063 (online), ISSN:0972-5210 STUDY ON EFFECTIVE METHODS FOR OIL PRODUCTS CLEANING Danehpash Shaghayegh 1, Farshchi Parvin 2*, Roayaei Emad 3, Ghoddousi Jamal 4 and Hassani Amir Hesam 5 1Department of Environmental Science, Faculty of Environment and Energy, Science and Research Branch, Islamic Azad University, Tehran, Iran. 2Department of Environmental Science, Faculty of Environment and Energy, Science and Research Branch, Islamic Azad UniversityTehran, Iran. *corresponding author 3Iranian National Oil Company,Tehran,Iran. 4Department of Environmental Management, Faculty of Environment and Energy, Science and Research Branch, Islamic Azad University, Tehran, Iran. 5Department of Environmental Engineering, Faculty of Environment and Energy, Science and Research Branch, Islamic Azad University, Tehran, Iran. *Corresponding Author Department of Environmental Science, Faculty of Environment and Energy, Science and Research Branch, Islamic Azad University, Tehran, Iran Abstract The hydrocarbon compounds which are discharged in to the environment are affected by various physical, chemical and biological alterations. Oil spill are a global concern due to the environmental impacts. The main concern of the environmental experts is the pollution from the production and transfer of oil products in different ecosystems. Among the consequences of releases of various types of crude oil, it is possible to mention the adverse environmental effects, the death of marine organisms, the inappropriateness of seafood for human consumption and the reduction of the power of flying sea birds due to the impregnation of feathers into petroleum products. The cost of oil remediation depends on relatively large parameters such as the type of oil products that leads to pollution, the amount and severity of the contamination, the time of the accident, the location of the incident, the geographical, political, economical, physical and biological location of the accident. -
CAMM Sidelights June 2016
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