scholarly journals UNITED STATES COAST GUARD ENVIRONMENTAL EMERGENCY RESPONSE CAPABILITY “THEN” AND “NOW”

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.

2001 ◽  
Vol 2001 (2) ◽  
pp. 1051-1054 ◽  
Author(s):  
Michael Adams

ABSTRACT The United States has several international oil pollution response agreements for which the U.S. Coast Guard serves as lead agency for implementation. However, the United States does not have an integrated plan for implementing these agreements, the criteria to use in determining what level of cooperation is needed, or a strategy for prioritizing which countries with which to engage to forge new agreements. This paper outlines a strategy for international engagement that allows the United States to participate in response-related expertise exchange to ensure appropriate capabilities are available for spills that threaten U.S. interests. Obstacles to developing and implementing the strategy and ways to overcome them also are identified.


2017 ◽  
Vol 2017 (1) ◽  
pp. 2017027
Author(s):  
Tim Gunter

Among the variety of oil spill response countermeasures, including mechanical, chemical, in-situ burning and bioremediation, deployment of chemical dispersants has been successfully utilized in numerous oil spills. This paper will review the history of the United States Coast Guard (USCG) C-130 Air Dispersant Delivery System (ADDS) capability, deployment in remote areas, and associated challenges. ADDS consists of a large tank with dispersant(e.g., 51,000 pounds), owned and operated by an industry partner, used aboard USCG C-130 aircraft designed to be ADDS capable as specified in various agreements for marine environmental protection missions. ADDS is a highly complex tool to utilize, requiring extensive training by air crews and industry equipment technicians to safely and properly deploy during an oil spill response. In 2011, the Commandant of the USCG, Admiral Papp reaffirmed the USCG's C-130 ADDS capability during a hearing before the Senate Committee on Commerce, Science, and Transportation, Subcommittee on Oceans, Atmosphere, Fisheries and the Coast Guard. The use of ADDS in remote areas creates unique challenges, such as logistical coordination between the USCG and spill response industry partners and maintaining proficiency with personnel. It is critical for federal, state, and local agencies, industry, and academia to understand the history and challenges of ADDS to ensure the successful utilization of this response tool in an actual oil spill incident.


Author(s):  
Helkei S. Hemminger

Abstract # —1141278 — In 2018, the Canadian government purchased the Trans Mountain pipeline, running from Alberta to British Columbia, along with the plans for expansion. The expansion could triple the transport capacity from 300,000 to 890,000 barrels of oil per day, and would increase the tanker traffic in the inland waterways of the Salish Sea, an area known for its sensitive marine habitat, and narrow, difficult to navigate passages. The anticipated increase in tanker traffic in this busy waterway continues to raise concerns about the impact of an oil spill and the financial means to address related injuries, particularly to natural resources. The transboundary nature of any spill further complicates the situation vis-à-vis the applicable liability regimes and response resources. Under the Canada-United States Joint Marine Contingency Plan (“JCP”), the United States Coast Guard and Canadian Coast Guard acknowledge each country's responsibility to fund their own response actions and pursue reimbursement of those costs within their respective jurisdictions. The availability of funding for a response, and to compensate injured parties, however, including the limits of liability of the responsible party, differs under each regime, and could impact the nature and scope of a response. For spills into or posing a substantial threat to the navigable waters of the United States, the Oil Pollution Act of 1990 governs and a national fund, the Oil Spill Liability Trust Fund (“OSLTF”), is immediately available to address an incident, including emergency restoration to natural resources. Canada's Marine Liability Act enables the Ship-source Oil Pollution Fund (“SOPF”) to pay claimants who have incurred damages as a result of oil pollution. Both countries' funds operate under the same principal—the polluter pays—but the compensation structure, and claims processes and procedures are entirely different. This paper provides an overview of these funding sources and claims procedures, comparing and contrasting the different systems. The discussion is meant to provide an overall understanding of potential funding pools available for spill responses under each scheme in order to facilitate transboundary spill planning and discussion.


2017 ◽  
Vol 2017 (1) ◽  
pp. 1345-1365
Author(s):  
Paul Meyer

Abstract 2017-321 The Department of the Interior’s Bureau of Safety and Environmental Enforcement (BSEE) National Oil Spill Response Research and Renewable Energy Test Facility, Ohmsett, plays a critical role in advancing oil spill response capabilities through research, development, testing, and training. Ohmsett’s 10 million liter (l) saltwater wave tank provides an independent venue to conduct research and development with full-size response equipment using real oil, in realistic, repeatable conditions. This paper will discuss recent research and development conducted at Ohmsett, including: Remote sensing of surface oil by BSEE, the National Oceanic and Atmospheric Administration (NOAA), the United States Army, the United States Coast Guard (USCG), and the United States Environmental Protection Agency (U.S. EPA); using acoustics to measure oil slick thickness; creating large volumes of emulsions for Ohmsett tests; mechanical recovery of chemically treated, undispersed oil; skimmer testing in diminishing slick thickness; a USCG and BSEE test of a skimmer ice management system; and an autonomous skimmer development. This paper will summarize the setup and methodology used during recent testing, training, and research conducted at Ohmsett. Reports of BSEE funded oil spill response research can be found at https://www.bsee.gov/site-page/master-list-of-oil-spill-response-research.


2021 ◽  
Vol 2021 (1) ◽  
pp. 684710
Author(s):  
Jim Elliott

Abstract The marine salvage industry plays a vital role in protecting the marine environment. Governments, industry and the public, worldwide, now place environmental protection as the driving objective, second only to the safety of life, during a marine casualty response operation. Recognizing over 20 years after the passage of the Oil Pollution Act of 1990 that the effectiveness of mechanical on-water oil recovery remains at only about 10 to 25 percent while the international salvage industry annually prevents over a million tons of pollutants from reaching the world's oceans, ten years ago the United States began implementing a series of comprehensive salvage and marine firefighting regulations in an effort to improve the nation's environmental protection regime. These regulations specify desired response timeframes for emergency salvage services, contractual requirements, and criteria for evaluating the adequacy of a salvage and marine firefighting service provider. In addition to this effort to prevent surface oil spills, in 2016, the U.S. Coast Guard also recognized the salvage industries advancements in removing oil from sunken ships and recovering submerged pollutants, issuing Oil Spill Removal Organization (OSRO) classification standards for companies that have the capabilities to effectively respond to non-floating oils. Ten years after the implementation of the U.S. salvage and marine firefighting regulatory framework, this paper will review the implementation of the U.S. salvage and marine firefighting regulations and non-floating oil detection and recovery requirements; analyze the impacts and effectiveness of these new policies; and present several case studies and recommendations to further enhance salvage and oil spill response effectiveness.


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.


2003 ◽  
Vol 2003 (1) ◽  
pp. 483-490 ◽  
Author(s):  
Dee Bradley ◽  
Mike Crickard ◽  
Carl Oskins ◽  
John Bradley

ABSTRACT Oil Spill Removal Organizations (OSROs) provide a necessary service to companies who produce, refine and transport (pipeline and road) oil and refined products and need to be prepared for the Worst Case Oil Spill Response Scenario. Those companies in coastal and near shore areas have virtually all of the classified OSROs to pick from, but such is not the case for oil companies located in the western areas of the United States. This paper looks at this dilemma through the experiences of one potential OSRO opting to target this inland operating area. Issues such as boom size; skimmer applications and ancillary equipment differences; different approaches to river, lake and stream spill response strategies; and the location of Captain of the Ports (COTPs) and Alternate City Classifications (ACCs) present unique challenges to providing inland OSRO support to companies who need it.


2003 ◽  
Vol 2003 (1) ◽  
pp. 913-917
Author(s):  
Michael Adams

ABSTRACT As called for under the International Convention on Oil Pollution Preparedness, Response and Co-operation, 1990 (OPRC), “Parties to the OPRC convention are required to establish measures for dealing with pollution incidents, either nationally or in co-operation with other countries.” As a signatory to OPRC the U.S. Government (USG) has pledged to assist other countries in the development of their own oil spill response capabilities and while USG has many agreements that meet the guidelines of assisting other countries, there is no formal engagement strategy for developing further agreements, no agency championing this effort, and there are many still requiring assistance. However, the United States Coast Guard (USCG) is uniquely positioned to perform the role of drafting an engagement strategy and working with the global community to assist those countries that have yet to develop an adequate oil spill response system of their own due to the lack of resources, expertise or both. There are many hurdles to enabling USCG to assume the OPRC assistance banner that have been previously addressed (Adams, IOSC 2001), which this paper will not seek to readdress. However, if USG does decide to move forward with an integrated policy there remains the need to develop an adequate engagement strategy. This strategy is necessary to ensure the limited resources available for foreign assistance are expended in the most cost effective, ethical and responsible manner possible. There are three alternative strategies I will analyze in an effort to determine the best suited for implementation of this policy. These three strategies are based primarily on 1) environmental need, 2) geographical proximity, and 3) political/economic interests. The goal of this strategy is to effectively implement the oil spill assistance policy alluded to previously in support of the U.S.'s pledge under OPRC. This paper will analyze the success of each strategy making a recommendation on which one USG should pursue.


1995 ◽  
Vol 1995 (1) ◽  
pp. 847-848
Author(s):  
David N. Lakin

ABSTRACT Limited liability for oil spill responders encourages aggressive actions that can maximize response efforts. The Marine Spill Response Corporation (MSRC), the world's largest oil spill response corporation, launched a nationwide campaign in 1991 to encourage the passage of responder immunity as contained in the Oil Pollution Act of 1990 in the coastal states and jurisdictions of the United States. As a national and not-for-profit organization, MSRC was a viable catalyst for successfully advocating the adoption of responder immunity. By the end of 1992, the 25 states/jurisdictions in MSRC's primary operating area had adopted responder immunity.


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