scholarly journals OPA 90: ENHANCED BY STATE PREVENTION AND RESPONSE PROGRAMS

2005 ◽  
Vol 2005 (1) ◽  
pp. 213-215
Author(s):  
K.C. Sullivan ◽  
Michael Baccigalopi ◽  
Dave Jensen

ABSTRACT In the wake of the Exxon Valdez the federal government passed the Oil Pollution Act of 1990 (OPA 90). A number of recent publications have discussed the effects of OPA 90 on the occurrence of unauthorized discharges, but nothing to date has included the additional influence of state regulations in their analysis. To address oil spill response on a state level, agencies such as the Texas General Land Office Oil Spill Prevention and Response Division (TGLO) and the Louisiana Oil Spill Coordinator's Office (LOSCO) were created. Each state, given authority under similar Oil Spill Prevention and Response Legislation, regulates heavily industrialized coastlines. These agencies have developed a level of expertise in management and response to oil spills that compliment the federal oil spill response capabilities. This programmatic analysis of two adjacent state agencies will show that the interaction between state government, industry, and the public has a large influence on the effectiveness of OPA 90.

1989 ◽  
Vol 1989 (1) ◽  
pp. 275-279 ◽  
Author(s):  
Laura Geselbracht ◽  
Jonathan Rubin ◽  
Thomas M. Leschine

ABSTRACT A state legislature sponsored study of Washington's oil spill damage assessment programs has revealed a number of problems. Studies designed to assess damages following major marine oil spills have not always been cost-effective and appropriate, state oil spill response activities have been difficult to fund, agencies have had difficulties spending damage recoveries in accordance with state law, and laws and regulations provide inadequate guidance on how to monetize resource damages identified. In addition, state agencies lack an alternative to field-based studies for compensation recovery in situations where damages are for all intents and purposes unquantifiable. An examination of CERCLA-based natural resource damage assessment procedures, the civil penalties in lieu of damages system employed by the State of Alaska, and other damage assessment practices had led to a recommendation for substantial changes in state marine resource damage assessment procedures. The recommended approach emphasizes the use of CERCLA-like preassessment screening to guide decisions about whether to quantify damages through field studies or to charge civil penalties in lieu of damages, as done in Alaska. In addition, emphasis is placed on direct negotiations with the responsible party to identify restoration/enhancement projects as alternatives to paying damages, and on developing capabilities to manage recovered damages and assessment costs through a new revolving fund.


1995 ◽  
Vol 1995 (1) ◽  
pp. 926-926
Author(s):  
Duane Michael Smith

ABSTRACT With the implementation of the Oil Pollution Act of 1990 came the requirement for vessels to develop plans for responding to oil spills from their vessels. While some companies had such plans in the past, the National Response System did not formally recognize their existence. Individual vessel response plans must now be viewed as an integral part of the National Response System. All of the parties that could be involved in an oil spill response must begin to view themselves as one tile of many that make up the mosaic known as the National Response System.


Resources ◽  
2021 ◽  
Vol 11 (1) ◽  
pp. 1
Author(s):  
Victor Pavlov ◽  
Victor Cesar Martins de Aguiar ◽  
Lars Robert Hole ◽  
Eva Pongrácz

Increasing exploration and exploitation activity in the Arctic Ocean has intensified maritime traffic in the Barents Sea. Due to the sparse population and insufficient oil spill response infrastructure on the extensive Barents Sea shoreline, it is necessary to address the possibility of offshore accidents and study hazards to the local environment and its resources. Simulations of surface oil spills were conducted in south-east of the Barents Sea to identify oil pollution trajectories. The objective of this research was to focus on one geographical location, which lies along popular maritime routes and also borders with sensitive ecological marine and terrestrial areas. As a sample of traditional heavy bunker oil, IFO-180LS (2014) was selected for the study of oil spills and used for the 30-year simulations. The second oil case was medium oil type: Volve (2006)—to give a broader picture for oil spill accident scenarios. Simulations for four annual seasons were run with the open source OpenDrift modelling tool using oceanographic and atmospheric data from the period of 1988–2018. The modelling produced a 30-year probability map, which was overlapped with environmental data of the area to discuss likely impacts to local marine ecosystems, applicable oil spill response tools and favourable shipping seasons. Based on available data regarding the environmental and socio-economic baselines of the studied region, we recommend to address potential threats to marine resources and local communities in more detail in a separate study.


1995 ◽  
Vol 1995 (1) ◽  
pp. 801-805
Author(s):  
Jonathan K. Waldron

ABSTRACT The Oil Pollution Act of 1990 (OPA 90) promoted a coordinated industry and government enhancement of response resources to combat oil spills effectively in the United States. However, the United States remains vulnerable to oil spills near the borders it shares with Canada, Mexico, and various nations in the Caribbean due to legal and administrative impediments associated with cross-boundary spill response activities. This paper explores cross-boundary related issues that could hinder a response and the relationship and roles of industry and government with regard to such issues, and provides recommendations to enhance improved cooperation between government and industry to facilitate response activities. The international structure that currently exists—globally, regionally, and bilaterally—provides a basic framework that promotes cooperation between nations to respond harmoniously to spills threatening the shores of neighboring countries. However, the existing agreements and understandings only provide a basic umbrella. They require planning and implementation of details and commitment to take the specific actions required to implement these agreements and understandings fully. As a result, the enhanced private response capability that now exists in the United States may not be available in a spill involving cross-boundary operations. Neighboring nations must take action to facilitate cross-boundary activities by responders by providing responder-immunity protection similar to that provided under OPA 90 and by removing potential impediments to response activities: laws and other requirements relating to matters such as customs, immigration, and safety training.


2014 ◽  
Vol 2014 (1) ◽  
pp. 2146-2158
Author(s):  
Allen R. Thuring

ABSTRACT This paper examines the oil pollution response fund created by Section 311(k) of the 1972 CWA and then modified, culminating with the Oil Spill Liability Trust Fund (OSLTF) established by OPA. Could the CWA have been successful absent the provision for a federal fund? This Fund is now four decades old. Has it passed the “test of time”? Did it meet the goals set at its birth? Is it still relevant? Should it continue? CWA Section 311 and later OPA created a range of response tools to deal with oil and hazmat spills on the waters of the US. They established a public/private solution to spill response. Key components:An expectation that the spiller was responsible and liable to clean up the spill;The National Contingency Plan and the Federal On-Scene Coordinator/FOSC;Establishing expertise on “special teams”: the CG's National Strike Force and EPA's Emergency Response Team;An up-front trust fund available only to the FOSC that pays for removals if the responsible party (RP) does not step forward. The fund exists to:Pre-empt the RP from using delay as a response option, despite the law.Give the FOSC money to quickly hire private response companies, if the RP does not act or if the spill's origin is a mystery. Equally important, the CWA and OPA did NOT designate a government agency to “clean up” oil spills. Rather, the law envisioned private companies performing that role, paid for by the spillers/RP or the 311(k)/OSLTF Fund, under the oversight of the USCG or the EPA. It tasked the USCG with managing this Fund. The Fund achieved its results. The US has a robust private oil spill removal sector that responsible parties hire when needed. If an RP does not act, the CG and EPA FOSCs use the Fund to mobilize those same companies to remove oil spills on US waters. The US economy has grown, as has the number of oil spills reported. Cases each year requiring Fund use have not increased proportionally. Responsible parties continue to clean up their spills, as the CWA envisioned. The Fund retains its ability to respond simultaneously to major spills, even during Exxon Valdez and Deepwater Horizon. In forty two years, the Fund has always been available for an FOSC directed removal. The opinions stated in this paper are the author's alone, and do not reflect the official policies of the United States Coast Guard.


2021 ◽  
Vol 937 (3) ◽  
pp. 032026
Author(s):  
R Akhtyamov ◽  
T S Titova ◽  
D V Glazkov ◽  
I I Gavrilin

Abstract The article provides an algorithm for organizing oil spill response on the water surface, as well as the results of the analysis of existing methods of oil and oil product spill response. In order to improve the complex of measures to eliminate oil spills on the water surface, the main requirements for oil-absorbing materials are given. It is shown that the localization and elimination of oil and oil products spills on the water surface due to the destruction of the underwater passage of the main oil pipeline requires a set of works that require the use of various methods and the use of the necessary technical means. The developed set of measures for organizing work in response to oil spills on the water surface and the results of the analysis of existing methods for responding to oil and oil products spills will reduce the time for containment and response to the spill, taking into account the optimal choice of technology for cleaning the coastal strip from oil pollution.


1989 ◽  
Vol 1989 (1) ◽  
pp. 215-219
Author(s):  
P. B. Ryan ◽  
D. J. S. Brown

ABSTRACT Oil spill contingency planning is concerned with the organization of preplanned responses to anticipated oil pollution emergencies in defined geographical areas. A major factor that must be considered when drafting any contingency plan is the support that can be expected from a variety of sources in times of emergency. Oil spills vary in both their magnitude and complexity and so do the responses to such incidents. It follows, therefore, that there is a tiered structure of oil spill contingency planning and response and that there is a corresponding tiering of sources of support. This paper identifies the various tiers of oil spill planning and response and reviews the external support relevant to each tier. The discussion base of this paper relates particularly to the ROPME sea area as defined herein but many of the observations will apply to other regions of the world where similar situations may be encountered.


1983 ◽  
Vol 1983 (1) ◽  
pp. 545-548
Author(s):  
Michael K. Breslin

ABSTRACT Oil pollution liability insurance surveys of oil handling installations are undertaken by insurance companies to qualitatively assess the chances that an oil spill will occur and the damage it could cause. By thus examining a facility, a basis is established on which to determine the premium for insurance coverage. In conducting such an oil spill risk assessment survey, many facets of oil handling and storage are considered, such as oil accounting, housekeeping, oil handling equipment, maintenance, outside contractor access and use, oil spill response equipment, and relationships with government agencies. Each facet must be addressed, and affects the final evaluation of the facility. Some of the procedures used for surface oil spills also can be applied to assess the risk of underground oil spills.


2003 ◽  
Vol 2003 (1) ◽  
pp. 919-922 ◽  
Author(s):  
T.H. Moller ◽  
F.C. Molloy ◽  
H.M. Thomas

ABSTRACT The International Convention on Oil Pollution Preparedness, Response and Co-operation, 1990 (OPRC Convention) defines the basic elements for co-operation between government and industry in marine pollution response. Emphasis is given in the Convention to developing contingency plans, equipment stocks, research and development initiatives, training and exercise programmes, and appropriate spill notification procedures for shipping. This paper reviews the current status of the partnership between government and industry for dealing with spills arising from the transportation of oil by sea. Three areas are explored: the risk of spills, environmental sensitivity issues, and the capabilities for dealing with oil spills in different regions of the world The format for the study is based on the Regional Seas and Partner Seas Programme initiated by the United Nations Environment Programme (UNEP), and supported by the International Maritime Organization (IMO). For each region, the main factors contributing to the risk of oil spills are identified, analysed and discussed in relation to the current pattern of oil transportation by sea. Comparisons are made with data on major oil pollution incidents drawn from ITOPF's oil spill database. Priorities and activities in the different regions are considered and the implications for oil spill response are discussed. Finally, the commitment and capabilities for mounting effective spill response measures in the different regions are gauged, with particular reference to the tenets of the OPRC Convention.


2021 ◽  
Vol 2131 (3) ◽  
pp. 032057
Author(s):  
R Akhtyamov ◽  
T S Titova ◽  
D V Glazkov ◽  
I I Gavrilin

Abstract The article provides an algorithm for organizing oil spill response on the water surface, as well as the results of the analysis of existing methods of oil and oil product spill response. In order to improve the complex of measures to eliminate oil spills on the water surface, the main requirements for oil-absorbing materials are given. It is shown that the localization and elimination of oil and oil products spills on the water surface due to the destruction of the underwater passage of the main oil pipeline requires a set of works that require the use of various methods and the use of the necessary technical means. The developed set of measures for organizing work in response to oil spills on the water surface and the results of the analysis of existing methods for responding to oil and oil products spills will reduce the time for containment and response to the spill, taking into account the optimal choice of technology for cleaning the coastal strip from oil pollution.


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