VESSEL RESPONSE PLANS: A TILE IN THE MOSAIC OF THE NATIONAL RESPONSE SYSTEM1

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.

1993 ◽  
Vol 1993 (1) ◽  
pp. 273-275 ◽  
Author(s):  
Lt. Alvin M. Crickard ◽  
Donald S. Jensen

ABSTRACT The Oil Pollution Act of 1990 (OPA 90) has resulted in an overall restructuring and enhancement of the national strike force. The OPA 90 legislation amended the Federal Water Pollution Control Act of 1972 (FWPCA), which first gave the Coast Guard a role in marine environmental protection. The FWPCA led to the establishment of the national response system (NRS) and the establishment of “special forces” which would be available for pollution response. These special forces included the Coast Guard manned strike teams (collectively, the national strike force, or NSF) and the public information assist team (PIAT). OPA 90 legislation affected the NSF by requiring the Coast Guard to establish a national response unit (NRU) located at Elizabeth City, North Carolina. The NRU, now renamed the National Strike Force Coordination Center (NSFCC), would provide overall management of the strike teams and PIAT and in addition, perform several new functions in consulting, exercise management, coordination of spill response, and logistics and maintenance of worldwide resource inventories. This paper examines all OPA 90 initiatives affecting the national strike force. It concludes that the overall impact on the national response system is quite positive and should result in significant improvement in response to both major and catastrophic oil spills.


2003 ◽  
Vol 2003 (1) ◽  
pp. 1035-1037 ◽  
Author(s):  
Michael Kirwan John Short

ABSTRACT On the 18th January 2000 a broken pipeline owned and operated by the oil company Petrobras spilt some 1300 tonne of bunker fuel into Guanabara Bay, Rio de Janeiro. The wildlife response was divided amongst 2 operational strategies and included – avian fauna and cetaceans. This paper deals with the cetacean response only. Cetaceans are generally not considered as an important feature of an oil spill response. Contingency planning for cetaceans in oil spills is now becoming an important element for preparedness for some countries. The cetacean response in Guanabara Bay specifically targeted a pod of about 70 members of the species Sotalia fluviatilis, a small dolphin that inhabits the bay. The response included the development of a plan that included a response system, a monitoring program and action plans. The response system detailed the mechanism for the plan to work and adopted the incident control management system. The monitoring program related to the study of any short term or long term deleterious effects resulting from the spill and consisted of basic spatial, temporal and behavioural studies. Action plans were developed specific to the character of Guanabara Bay and included the rescue and rehabilitation strategies necessary to respond to oil affected cetaceans. A training program was then developed and implemented to personnel who were to enact the cetacean response.


2017 ◽  
Vol 2017 (1) ◽  
pp. 2879-2894
Author(s):  
Christopher Klarmann ◽  
LCDR Johna Rossetti

ABSTRACT ID: 2017-101 – GIUEs: Developing Best Practices to Improve Marine Environmental Response Preparedness The U.S. Coast Guard (USCG) is authorized by the Oil Pollution Act (OPA) of 1990 to conduct Government Initiated Unannounced Exercises (GIUE), a cornerstone of the oil spill exercise cycle. These exercises are instrumental for USCG Captains of the Port (COTP) to evaluate industry preparedness for oil spill response by specifically testing a facility or vessel on notification procedures, response time, and deployment of facility-owned or Oil Spill Removal Organization (OSRO) equipment. Facility Response Plan holders and Vessel Response Plan holders are subject to these exercises under federal regulations 33 C.F.R. § 154 and § 155. In 2013, the USCG restructured their GIUE policy to provide better guidance for employees. This updated policy detailed how to properly plan and conduct a GIUE as well as established expectations following both satisfactory and unsatisfactory exercises. In this paper we will examine the changes that the USCG has made regarding its policy on planning and conducting GIUEs, describe how USCG field units are implementing the new policy, including how unsatisfactory GIUEs are addressed, and examine what commonalities, are being seen in GIUE unsatisfactory results. Finally, we will discuss how plan holders, OSROs, and regulatory agencies can work together to better prepare for responding to an environmental emergency when it occurs.


1991 ◽  
Vol 1991 (1) ◽  
pp. 695-697
Author(s):  
David M. Bovet ◽  
Charles R. Corbett

ABSTRACT The Oil Pollution Act of 1990 establishes a system of oil spill liability, compensation and financial responsibility at levels not contemplated prior to the Exxon Valdez incident. Furthermore, it does so while preserving states’ prerogatives and rejects the international solution embodied in the 1984 Protocols to the 1969 Civil Liability and 1971 Fund Conventions. The act requires new contingency planning by both industry and government and sets new construction, manning, and licensing requirements. It increases penalties, broadens enforcement responsibilities of the federal government, and enhances states’ participation in the national response program. It also establishes a billion dollar federal trust fund to supplement the liability of responsible parties. The act is likely to result in safer tanker operations and to reduce the threat of oil spills in U.S. waters. These environmental improvements will be paid for by U.S. oil consumers. Other implications include the following:Reassessment of involvement in U.S. oil transportation by both independents and oil majorsEnhanced preparedness by responsible partiesA gradual rise in freight ratesCorporate restructuring to shield liabilityFewer small oil companies and independent carriers in U.S. tradesPotential disruptions linked to new certificates of financial responsibilityPotential shortages of Alaskan trade tonnageHeightened presence of state governments in oil spill incidents, oil spill legislation, and enforcement


2014 ◽  
Vol 2014 (1) ◽  
pp. 1431-1440 ◽  
Author(s):  
Marcus Siewert ◽  
Martin Powilleit ◽  
Fokke Saathoff

ABSTRACT The success of oil spill response operations is mainly dependent on the response time and the weather and sea state conditions. That's where the research project “BioBind” is setting the focus: To develop an oil spill response system fast to apply and sea state independent. Within this project a network of eight different partners from universities, research institutes and medium sized companies work from summer 2011 to summer 2014. The paper provides an overview on the oil spill response research project “BioBind” and focuses on a large scale field experiment carried out in summer 2013 with the RV “E.M.Borgese” at the Baltic Sea.


2017 ◽  
Vol 2017 (1) ◽  
pp. 2017108
Author(s):  
A J M Gunasekara

The total volume of oil spilled and the number of spills has declined significantly over the past forty years. However, oil spills are no longer considered as an unavoidable. The ship source oil pollution still remains a potentially important risk to the local economies and the marine environment which can cause major economic loss and severe damages to the coastal and marine environment. The international regulatory framework to deal with liability and compensation in the event of ship source oil pollution has evolved over the past three decades. The available international legal regime for oil pollution liability and compensation is playing a great role in governing a discharge of oil into the sea by ensuring liability for polluters and compensation for victims of pollution. Despite the fact that the total cost of the oil spill cannot be compensated through the available international civil liability regime and entire damages caused to the marine environment cannot be compensated or recovered. This paper examined the application and limitations of available liability and compensation mechanism for the protection marine pollution and compare the benefit of the establishment of a funding mechanism for the strengthening of the level of oil spill preparedness and the civil liability regime for the protection of the coastal and marine environment. In addition, this paper reviews the funding mechanism adopted by the countries to the strengthening the level of oil spill preparedness taken into account the polluter pays principle without a putting extra burden for the general taxpayers. The establishment of a system for the funding of oil spill preparedness using the polluter pay principle has immensely helped to improve the oil spill response capabilities and protection of the marine environment of coastal states which adopted a unique funding mechanism by applying the polluter pay principle. This paper recommends the among other thing review the available compensation and liability regime for the protection of the marine environment and recommend to adopt and apply a uniform funding mechanism for the strengthening of the level of oil spill preparedness taken into account the polluter pay principle for the protection of the marine environment and improve the status quo.


1997 ◽  
Vol 1997 (1) ◽  
pp. 453-457 ◽  
Author(s):  
CDR Robert A. Van Zandt

ABSTRACT The Coast Guard's oil spill removal organization (OSRO) classification process underwent significant revision in late 1995. The revision was necessary to strengthen the program into a more credible and useful tool for facilitating preparation and review of vessel and facility response plans. The revised process is more closely linked to the response planning criteria that vessel and facility owners and operators are required to meet under the Oil Pollution Act of 1990. As a result, the process provides a better indication of an OSRO's capacity and potential to respond to and recover oil spills of various sizes. Data provided by each OSRO are being included in the computer-based national Response Resource Inventory (RRI). The paper describes the important features and limitations of the revised classification process and gives an interpretation of what the new classifications mean to response plan holders and reviewers. It also describes the method by which plan holders can use the computer-based RRI as a tool to conduct their own analysis of an OSRO's capacity to meet their specific planning requirements.


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.


2001 ◽  
Vol 2001 (1) ◽  
pp. 693-697
Author(s):  
Tina M. Toriello ◽  
Jan Thorman ◽  
Pamela Bergmann ◽  
Richard Waldbauer

ABSTRACT This paper focuses on industry and government roles for addressing historic properties during oil spill response. In 1997, the National Response Team (NRT) developed a Programmatic Agreement on Protection of Historic Properties during Emergency Response under the National Oil and Hazardous Substances Pollution Contingency Plan (PA) (National Response Team, 1997). At the 1999 International Oil Spill Conference (IOSC), U.S. Department of the Interior (DOI) representatives discussed the development and implementation of the PA, which is intended to ensure that historic properties are appropriately taken into account during the planning for and conducting of emergency response to oil spills and hazardous substance releases. Following the 1999 IOSC, DOI and Chevron representatives began a dialog regarding industry and government roles under the PA. Chevron invited the DOI representatives to participate in an October 1999 large-scale, industry-led spill exercise; a precedent-setting drill that included historic properties protection as a key objective. This 2001 paper focuses on how industry and government have worked together to protect historic properties, government roles in PA implementation, and lessons learned. As an example of what industry can do to support the protection of historic properties during planning and response activities, this paper describes Chevron's Historic Properties Program, a program managed under its emergency spill response environmental functional team (EFT). A discussion of lessons learned focuses on the need for clear definition of industry and government roles, and the benefits of building a foundation of cooperation between industry and government to protect historic properties. Of particular importance is the inclusion of historic properties in all aspects of oil spill preparedness and response, including planning, drills, training, and response organization structure and staffing. Experience from incident response in Alaska has shown that the PA assists Federal On-Scene Coordinators (FOSCs) and responsible parties, while also protecting historic properties, when the FOSC is prepared to implement the PA promptly and effectively.


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