CONTINGENCY PLANNING, CONTRACTOR REQUIREMENTS, AND OIL POLLUTION ACT OF 1990 IMPLEMENTATION

1993 ◽  
Vol 1993 (1) ◽  
pp. 51-56
Author(s):  
Joseph E. Lees

ABSTRACT In response to widespread public concern, Congress enacted the comprehensive Oil Pollution Act of 1990. This, in addition to legislation enacted by many coastal states, will bring dramatic changes to oil spill response in the United States. This paper considers OPA 90's response planning requirements, the rule-making process for implementing these requirements, and key issues in response planning. It compares the proposed federal requirements with state response planning and contractor requirements. The response planning system faces a long period of adjustment. Sustained efforts will be needed to harmonize the many state and federal laws and regulations into a coherent, consistent, and understandable response regime.

1993 ◽  
Vol 1993 (1) ◽  
pp. 643-648 ◽  
Author(s):  
Amy M. Stolls

ABSTRACT Because the federal Oil Pollution Act of 1990 (OPA 90) allows state preemption, vessel and facility owners that operate in the United States know that simply complying with federal laws and regulations is not enough. Though some states have enacted legislation similar to OPA 90 and have taken a wait-and-see approach to the promulgation of regulations, many others did not wait for federal agencies to resolve certain issues. This paper reviews new state oil spill laws and regulations in the coastal United States and compares their approaches to contingency planning, prevention, responder immunity, financial responsibility, liability, and other key issues.


2014 ◽  
Vol 2014 (1) ◽  
pp. 299560
Author(s):  
Rhonda Murgatroyd ◽  
Alexis Kott ◽  
Lawrence Malizzi

The last days of August 2012 brought Hurricane Isaac's wind and water energy to south Louisiana impacting many parishes with destruction of property and leaving behind severe flooding, making response difficult in some locations. After search and rescue efforts ensuring safety of the people in the areas had been completed, surveys by boat and aircraft began to reveal impacts to wildlife from petroleum product of unknown origin. As in past natural disaster response activations, wildlife professionals expected oil impacted animal cases to remain minimal; however, there was confirmation from some response crews on site that there were in fact affected animals. Given that there was no named Responsible Parties, the United States Coast Guard (USCG), as the Federal On-Scene Coordinator (FOSC), took the lead in activation of the Oil Spill Response Organizations (OSROs) and the wildlife personnel to conduct recovery and rehabilitation efforts in coordination with the State of Louisiana. All costs associated with these activities were covered by the National Pollution Funds Center (NPFC), which is managed by the USCG as promulgated under the Oil Pollution Act of 1990 (OPA 90). Wildlife Response Services, Inc. (WRS) supported by Matrix New World Engineering, Inc. (Matrix), was mobilized on September 2, 2012 to set up a Wildlife Rehabilitation Center (Center) in Belle Chase, Louisiana. The Center was set up in the Bricor Trucking Warehouse and the team had the Center operational the morning of September 3, 2013and received its first animal in the afternoon of that same day. During the response the Louisiana Department of Wildlife and Fisheries (LDWF) was responsible for oiled wildlife recovery and transport to the Center. Over the course of the response 7 live animals were cared for, most of which were cleaned and eventually released back into the wild. The Hurricane Isaac response demonstrated the leadership of the USCG in organizing oiled wildlife recovery and rehabilitation jointly with LDWF and WRS, as well as with the OSROs. This is a model for responses to future natural disasters.


1999 ◽  
Vol 1999 (1) ◽  
pp. 635-638
Author(s):  
William C. Rogers ◽  
Jean R. Cameron

ABSTRACT Oil shipping companies operating on the West Coast of the United States are subject to international, federal, and state oil spill prevention and response planning regulations. Many companies wrote separate plans for each jurisdiction with the result that tank vessels carried several different plans on board and parent companies faced an administrative burden in keeping plans current. In June 1996, oil shipping company representatives proposed that the States/British Columbia Oil Spill Task Force work with them to develop a format incorporating West Coast states' and U.S. Coast Guard contingency planning requirements. A workgroup comprised of representatives of the Task Force, industry, and the U.S. Coast Guard, working cooperatively, eventually proposed a voluntary integrated plan format based on the key elements of the U.S. Coast Guard Vessel Response Plan. This format allowed correlation with state planning requirements as well as with the Shipboard Oil Pollution Emergency Plan (SOPEP) required by international regulations. The U.S. Coast Guard, the Canadian Ministry of Transport, and all West Coast states have subsequently documented their agreement to accept vessel plans in this format, to coordinate review as needed, and to allow references to public documents such as Area Plans.


2001 ◽  
Vol 2001 (1) ◽  
pp. 3-24 ◽  
Author(s):  
Gary Tannahill ◽  
Alexis Steen

ABSTRACT Since its inception, the Oil Pollution Act of 1990 (OPA 90) was intended to greatly improve the ability to respond to large spills in the United States and has been the subject of frequent discussion and debate within the United States and elsewhere. Its provisions created new regulatory programs, expanded existing requirements, and established a variety of competency requirements for those entities and personnel involved in the production, transport, handling, or storage of petroleum within the United States. Tens upon tens of articles have been published in prior Proceedings of the International Oil Spill Conference (IOSC) and in many other venues about legislative intent, subsequent regulatory programs and their implementation, interagency negotiations, industry compliance successes or difficulties, training issues, etc. OPA 90 has also had an impact on U.S. policies internationally and in U.S. participation in international spill conventions/treaties. In recognition of a decade's passage since its enactment, IOSC sponsors commissioned a review and analysis of the effectiveness of OPA 90 and the interrelationship of OPA 90 with other oil spill laws and rules in the world. Another important purpose was to identify issues for the related panel discussion of this topic at the 2001 IOSC. This review was conducted using a questionnaire to acquire input from a broad range of individuals with OPA 90 expertise and experience. An informal survey of 57 questions in four sections was prepared and distributed to 22 participants. These participants were selected to represent a core of knowledge about OPA 90 and its history of implementation. Findings from the survey are presented to foster discussion and debate, educate members of the spill response community, assist with resolution of outstanding issues, and help focus on future issues that will need attention. The rate of response to the survey questions was high and enabled a broad review of the effectiveness of some of the various OPA 90 requirements. Questions were in either multiple-choice or essay format. Commonalties, differences, and issues were identified from all responses and used to evaluate OPA 90. From the commonalties and differences in the responses, selected OPA 90 requirements were classified as effective or ineffective. Based on an analysis of multiple-choice and essay answers, respondents generally agreed that OPA 90 was moderately effective (across all covered provisions). Closer examination of the four survey sections, however, indicated distinct concerns and benefits derived from implementation of OPA 90. In addition, where OPA 90 provisions were judged effective, caveats sometimes followed. Despite the effective rating of many OPA 90 prevention provisions, prevention still needs more attention based on the opinions of the survey respondents. Some respondents felt more attention and resources often are given to preparing to respond to a spill than to preventing spills, even though preventing a spill is considered preferable. Further, some believed that spill prevention would be enhanced if vessels with large, onboard bunker fuel storage also were subject to prevention requirements similar to OPA 90 requirements for vessels carrying petroleum as cargo. Survey feedback indicated that better Area Contingency Plans (ACPs) could result in significant improvements in response preparedness. ACPs need to be improved in many geographic areas. ACPs should be more response-oriented and less like a reference document, and be made more readily available and useable. Many respondents viewed these items as the foundation for any major improvements in response planning. In the United States, spill response using a multiparty management system, which is inclusive of broad stakeholder groups, differs from systems in other countries. Most felt that response activities can impact restoration activities greatly, but the legal structure does not support a seamless and efficient coordination of response and restoration. Coordination between response and restoration needs to be improved to avoid response delays and promote better/faster resource restoration. The biggest concern expressed by survey respondents regarding restoration dealt with management of the Natural Resource Damage Assessment (NRDA) process. Damage assessments and restoration management need to be streamlined, partly because too many interested parties make decision making inefficient. Some felt that public review of restoration plans led to better results; others felt public review delayed timely restoration activities. While international cooperation has increased over the last decade, respondents felt there was room for further improvement. In particular, sharing personnel and resources better, joining inspection and control programs, and drafting international restoration guidelines were some of the improvement activities mentioned. Findings from this survey have provided insights on what actions are needed to further improve spill prevention, preparedness, response, and restoration. Now is the time to renew this effort and improve performance to a higher plane globally. 2001 IOSC sponsors and Issue Paper Subcommittee desire the response community's commitment and solicit its involvement toward this goal.


2014 ◽  
Vol 2014 (1) ◽  
pp. 1881-1898 ◽  
Author(s):  
Bradford Benggio ◽  
Debra Scholz ◽  
Dave Anderson ◽  
Joseph Dillon ◽  
Greg Masson ◽  
...  

ABSTRACT In the United States (U.S.), oil spill response planning, preparedness, and response requirements are dictated primarily by the National Oil and Hazardous Substances Pollution Contingency Plan, a regulation that implements the Oil Pollution Act of 1990, the Clean Water Act, and the Comprehensive Environmental Response, Compensation and Liability Act. At the planning stage, these regulations require the development of national, regional, and local response capabilities and promote overall coordination among responders. During a spill, these capabilities are utilized by the Federal On-Scene Coordinator (FOSC) to analyze whether response actions are likely to impact protected resources. The consultation process required under Federal statutes, charges the FOSC to consult with Federal, state, Tribal entities, and other Federal agencies to determine potential effects of response actions during an incident and to develop strategies to avoid, minimize, and mitigate those effects (40 CFR § 300.135(j); § 300.305(e); and § 300.322(a), 1994). Consultations should continue until response operations are concluded and may continue after operations are complete. Four key regulatory mandates that require an FOSC to initiate consultation during a response include:Endangered Species Act of 1973, as amended requires consultation with US Fish and Wildlife Service (USFWS) and the National Marine Fisheries Service (NMFS) on federally listed species and designated critical habitats;Magnuson-Stevens Act requires consultation with NMFS on any action that may affect Essential Fish Habitats;National Historic Preservation Act of 1966, as amended requires Federal agencies to consult with states, federally recognized tribes, and other stakeholders on potential impacts to historic and cultural resources; andTribal Consultations under Executive Order 13175 – Consultation and Coordination with Indian Tribal Governments when federally recognized Indian Tribes and their interests are affected by a response. Consultation is also required under the Native American Graves Protection and Repatriation Act when Native American burial sites, human remains, funerary objects, sacred objects, or items of cultural patrimony are identified on Federal or Tribal lands during a response and no pre-consultation plan of action has been developed.1 Consultation requirements are not universally understood, leading to uncertainty and inconsistencies across the response community and Trustees regarding when to initiate and how to conduct the consultations. This paper discusses the Federal consultation requirements and identifies areas of possible uncertainties in the consultation process throughout the pre-spill planning, response, and post-response phases of an incident. This paper will suggest resolutions and recommendations to further enhance the consultation process by the Federal spill response decision-makers and planning bodies.


2014 ◽  
Vol 2014 (1) ◽  
pp. 1569-1582
Author(s):  
Hugo Nijkamp ◽  
Saskia Sessions ◽  
Philippe Blanc ◽  
Yannick Autret

ABSTRACT The Arctic is an extremely vulnerable area for oil pollution. Because of global warming and the resulting retreating ice, new economic shipping and Exploration & Production activities are likely to develop in the coming years and decades. Both governments (e.g. Arctic Council) and the oil industry (e.g. Arctic Response Technology Joint Industry Programme) are preparing for increased oil spill response capabilities in the Arctic region, and are looking to join forces for more efficiency and effectiveness. In connection to oil spill response planning in the Arctic both onshore and offshore, attention should be given to oiled wildlife response preparedness in this region. The Arctic is characterized by unique ecosystems and biodiversity, either marine or terrestrial, with a large proportion of migratory species. So although species diversity is assumed to be low compared to other regions, Arctic wildlife is very sensitive to the effects of oil pollution. Additionally the Arctic is a remote and extreme area for setting up a wildlife response in the framework of an oil spill response. This paper explores what the limitations of an Arctic oiled wildlife response would be (physical/logistical, health & safety, environmental monitoring, ecosystems understanding, biodiversity data, sensitivity mapping, etc.), and identifies how current gaps in response preparedness could be filled. Special emphasis is laid on investments into the capabilities of specialised responders and their equipment, including creation of a specialised Arctic Wildlife Response Strike Team.


1997 ◽  
Vol 1997 (1) ◽  
pp. 761-764 ◽  
Author(s):  
Dana Stalcup ◽  
Gary Yoshioka ◽  
Brad Kaiman ◽  
Adam Hall

ABSTRACT In the years following the passage of the Oil Pollution Act of 1990 (OPA 90), government agencies and regulated parties in the United States have begun to implement spill prevention and preparedness programs. For this analysis, 7 years of oil spill data collected in the Emergency Response Notification System were used to measure the impact that OPA 90 has had on preventing large spills. Furthermore, relationships among the types, sources, and location of spilled oil are characterized. A comparison of the number of reported 10,000-gallon oil spills for the years 1992-1995 to that number for the years 1989-1991 indicates a decline, not only for vessels but also for pipelines and fixed facilities. The decline in large oil spills to water from various sources appears to indicate that the efforts of government and industry have had a measurable impact on environmental protection.


2003 ◽  
Vol 2003 (1) ◽  
pp. 491-496 ◽  
Author(s):  
Jon Rødal ◽  
Frode Engen ◽  
Kåre L. Jørgensen ◽  
Geir M. Skeie

ABSTRACT In 2001, the Norwegian Clean Seas Association For Operating Companies (NOFO) completed a three year R&D-program for development of a dynamic, risk based oil spill response regime for the entire Norwegian continental shelf, including coastal areas and the shoreline. A central element of the new regime is an oil spill contingency planning system, where all relevant information are made fully available on the Internet. The web based Oil Spill Contingency Planning System (OSCPS) has proved to be an important and useful result of the project, and the responses from authorities as well as stakeholders have been positive. The system contains guidelines and standards that have been adopted by the industry, resulting in standardized and comparable site specific analyses. In addition to the information available on the Internet, a suite of Geographical Information System (GIS) tools have been developed and made available for all NOFO member companies. These tools have proved useful in analyses, training and desktop exercises. This paper provides an overview and highlights of our new OSCPS and Geographical Information System (GIS) tools, presenting examples of use and lessons learned. The paper also presents the responses from authorities and stakeholders to this open and transparent approach.


2008 ◽  
Vol 2008 (1) ◽  
pp. 459-461
Author(s):  
Leonard Rich

ABSTRACT The intent of the Oil Pollution Act of 1990 (OPA90) is to ensure the U.S. Government is prepared to protect the environment from a catastrophic spill of the magnitude and complexity of the 1989 EXXON VALDEZ oil spill. The OPA90 legislation resulted in an overall restructuring and enhancement of the National Strike Force (NSF), and establishment of District Response Groups who are staffed and equipped with mechanical spill recovery assets and are prepared to take prompt actions to mitigate a worst case discharge scenario. During the early 1990s, over $31 million dollars worth of oil spill response equipment was acquired and placed at 23 locations throughout the United States. Since then, an additional $10 million dollars of environmental emergency response equipment has been added to the USCG'S inventory, and are now located at 16 additional sites. This paper will elaborate on the evolution of the USCG'S environmental emergency response capabilities. In terms of preparedness, it will explain how, where and why the Coast Guard has adjusted its resources and capabilities since the OPA90 legislation. The expanded mission requirements include; redistributing and adjusting the locations of the Vessel of Opportunity Skimming Systems, expanding functional use of the pre-positioned equipment for dewatering during shipboard fires, designing and implementing an offload pumping system for viscous oil at each NSF Strike Team, revisiting the condition and continued use of OPA90 procured first response “band-aid’ equipment, modifying the basic response equipment systems for fast current spill response, and the implementation of the Spilled Oil Recovery System. These actions reflect policy and mission adjustments influenced by an ever changing environment. The Coast Guard has re-organized from the bottom up to meet increased port security measures, and the capability to respond to all-hazard incidents. We must continue to maintain a high state of readiness in the oil spill response environment and accept the need to incorporate change to the equipment and the way we conduct our support to the American public.


Author(s):  
Chrystin McLelland ◽  
Haley Kennard

Abstract: The Northwest Region (the states of Washington, Oregon, and Idaho) of the United States is home to 43 federally recognized treaty Tribes, who are resource co-managers within their traditional territories and have both decision-making power and sovereign legal rights. There is also a significant refinement and transportation of petroleum products (by rail, pipeline, and vessel) within this area and in our transboundary waters. In Washington alone, more than 20 billion gallons are moved through and across the state on an annual basis. The Northwest Area Committee (NWAC) and Region 10 Regional Response Team (RRT10), the federally mandated bodies which conduct oil pollution and hazardous materials spill response planning, are therefore robust and very active. Within the last decade, tribal engagement in the NWAC and RRT10 has expanded significantly; the RRT10 now has three official tribal members, and the NWAC has supported a Tribal Engagement Task Force for the past four years and is currently looking at transitioning it to a longer-term and more permanent sub-committee strategy. This presentation will discuss the following pieces of the efforts towards tribal engagement in the NWAC/RRT10: 1) The evolution of tribal engagement in the RRT10/NWAC and lessons learned from this process 2) A case study of the unique experience of the Makah Tribe's engagement with the greater response community including both becoming the first tribal member of the NWAC/RRT10 and the development of their memorandum of agreement with the US Coast Guard, and 3) Results from the 2019 Tribal Engagement Task Force's tribal feedback survey (sent out to all Tribes in the region) to identify barriers and strategies for improved meaningful tribal engagement. This reflects the commitment of the NWAC/RRT10 to improving tribal engagement by understanding; the results can not only inform partners in other regions but will inform the next phase of the NWAC/RRT10's approach to tribal engagement. The Northwest Area model for tribal engagement in oil spill planning, preparedness, and response is an important precedent for national and international engagement with Indigenous peoples in this arena.


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