Selecting a Preferred Restoration Alternative for the Julie N Oil Spill

1999 ◽  
Vol 1999 (1) ◽  
pp. 1089-1092
Author(s):  
Timothy J. Reilly ◽  
Frank Csulak ◽  
Paul Van Cott

ABSTRACT The selection of preferred restoration alternatives during the restoration planning phase of a natural resource damage assessment occurs through the implementation of a multifaceted process. This process requires identifying the nature and extent of resources injured by an oil spill; identifying appropriate restoration alternatives which address the resources injured, scaling the restoration alternatives to quantified injuries and selecting the most appropriate restoration option(s) for implementation with appropriate public participation. The Trustee Council for the Julie N oil spill, occurring in Portland Harbor, Maine, on September 27, 1996, is currently undergoing this process. This paper presents the major activities associated with selecting the preferred restoration options, and offers lessons learned to date, regarding the implementation of this process.

1993 ◽  
Vol 1993 (1) ◽  
pp. 727-731
Author(s):  
Randall B. Luthi ◽  
Linda B. Burlington ◽  
Eli Reinharz ◽  
Sharon K. Shutler

ABSTRACT The Damage Assessment Regulations Team (DART), under the Office of General Counsel of the National Oceanic and Atmospheric Administration (NOAA), has centered its efforts on developing natural resource damage assessment regulations for oil pollution in navigable waters. These procedures will likely lower the costs associated with damage assessments, encourage joint cooperative assessments and simplify most assessments. The DART team of NOAA is developing new regulations for the assessment of damages due to injuries related to oil spills under the Oil Pollution Act of 1990. These regulations will involve coordination, restoration, and economic valuation. Various methods are currently being developed to assess damages for injuries to natural resources. The proposed means include: compensation tables for spills under 50,000 gallons, Type A model, expedited damage assessment (EDA) procedures, and comprehensive procedures. They are being developed to provide trustees with a choice for assessing natural resource damages for each oil spill.


1997 ◽  
Vol 1997 (1) ◽  
pp. 851-854
Author(s):  
Frank Csulak ◽  
Douglas Helton ◽  
Carol-Ann Manen ◽  
Norman Meade ◽  
Marguerite Matera

ABSTRACT On January 19, 1996, the tank borge North Cape and the tug Scandia grounded on Moonstone Beach in southern Rhode Island, spilling 828,000 gallons of no. 2 heating oil into Block Island Sound. Just 2 weeks prior to the grounding, the National Oceanic and Atmospheric Administration (NOAA) had published the final natural resource damage assessment (NRDA) rule for the Oil Pollution Act of 1990 (OPA). The North Cape oil spill became the first opportunity to implement the new NRDA rules. One of the key provisions of the NRDA rule is the requirement that trustees must invite the responsible parties (RP) to participate in a cooperative assessment of damages. If the trustees and the RP can agree to perform the initial phases of an assessment cooperatively, the chances of achieving a fair settlement and avoiding protracted litigation are expected to be enhanced. The cooperative approach should also reduce overall transaction costs, facilitate settlement, and result in a more rapid implementation of restoration projects. This paper presents an overview of the cooperative natural resource damage assessment process being undertaken by the trustees and the RPs following the North Cape oil spill and highlights some of the lessons learned in conducting a cooperative assessment.


1995 ◽  
Vol 1995 (1) ◽  
pp. 333-338
Author(s):  
Douglas Helton ◽  
Donna Lawson ◽  
Martin McHugh

ABSTRACT On June 24, 1989, the Uruguayan merchant marine tanker Presidente Rivera, loaded with 19 million gallons of No. 6 fuel oil, ran aground in the Delaware River near Marcus Hook, Pennsylvania, spilling between 200,000 and 300,000 gallons of oil. Currents spread the oil over approximately 29 miles of shoreline in New Jersey, Delaware, and Pennsylvania, reaching upstream as far as Little Tinicum Island, a wildlife refuge near Philadelphia, and downstream as far as Reedy Island, south of the Chesapeake and Delaware Canal. Natural resources under the trusteeship of New Jersey, Delaware, Pennsylvania, the U.S. Department of the Interior, and the National Oceanic and Atmospheric Administration (U.S. Department of Commerce) were affected by the spill, including shoreline parks, fisheries, marshes, birds, and wildlife. Additionally, portions of the river were closed to vessel traffic and nearby creeks were boomed off, preventing access to marinas and boat ramps. After three years of damage assessment, pretrial discovery, and negotiations, the trustees reached a settlement on natural resource damages with the responsible party. This paper discusses the strategy used by the trustees in developing a natural resource damage claim and highlights some of the lessons learned during the assessment and settlement process.


1987 ◽  
Vol 1987 (1) ◽  
pp. 533-540
Author(s):  
Gary L. Ott

ABSTRACT Federal guidelines that outline a process for natural resource damage assessment have recently been published. The guidelines provide two types of assessment procedures that are referred to as Type A assessments and Type B assessments. The Type A procedures are for simplified assessments and use a computer model to measure in monetary terms compensation for injury to marine and coastal natural resources through the use of average values and approximations. The proposed Type A computer model was used to analyze a major oil spill that occurred in Island Park, New York, where the federal on-scene coordinator had attempted to evaluate the magnitude and severity of the spill. In this one instance, both field observations and the proposed Type A computer model characterized this major oil spill as having a limited impact on the environment. Oil and chemical spills are generally characterized only by the size of the release. Conceivably, the proposed Type A model could be used as a tool for characterizing a spill by its potential to injure natural resources. The ability to focus on the environmental impacts of a spill may help analyze response actions that reduce natural resource damages.


1995 ◽  
Vol 1995 (1) ◽  
pp. 905-906
Author(s):  
Carlos Villoria ◽  
Rosa Pérez

ABSTRACT In 1991, the Venezuelan oil industry, through INTEVEP, its research and development subsidiary, started a project to implement an oil spill decision support system (DEPET 4.0) for the Venezuelan national oil spill contingency plan. For this primary tool for taking spill response actions in operational drills and real emergencies, the industry developed a database of possible scenarios in predetermined sites and for natural resource damage assessment. The system covers the entire Venezuelan coastline, with each of five management zones serviced by a separate base map and data.


1995 ◽  
Vol 1995 (1) ◽  
pp. 948-949
Author(s):  
Mark B. Garcia

ABSTRACT The Office of Oil Spill Prevention and Response (OSPR), the Department of Fish and Game, is the lead state agency charged with oil spill prevention and response in the marine environment of the state of California. The OSPR was established pursuant to the California Oil Spill Prevention and Response Act of 1990. The legislation provides the OSPR Administrator with substantial authority to direct spill response, cleanup, and natural resource damage assessment activities.


1993 ◽  
Vol 1993 (1) ◽  
pp. 711-716 ◽  
Author(s):  
William H. Desvousges ◽  
Richard W. Dunford ◽  
Kristy E. Mathews ◽  
H. Spencer Banzhaf

ABSTRACT The natural resource damage assessment (NRDA) methods used to estimate the damages from the Arthur Kill oil spill employed a transfer methodology. The base-case estimate for use damages was $46,000 and for non-use damages was $525,000.


2005 ◽  
Vol 2005 (1) ◽  
pp. 95-99 ◽  
Author(s):  
James H. Jeansonne ◽  
Thomas Moore ◽  
David Bernhart ◽  
Melissa Snover

ABSTRACT Following a mystery oil spill near Ft. Lauderdale, Florida in August 2000, natural resource trustee agencies (Trustees) conducted a natural resource damage assessment (NRDA) under the Oil Pollution Act of 1990 (OPA). During the NRDA, injury to several life stages of Loggerhead sea turtles (Carena caretta) and Green sea turtles (Chelonia my das) was quantified using a computer model, SIMAP (French-McCay, 2001), and the type and scale of restoration required was determined. Quantification of injury required Trustees to determine key model input parameters based on a variety of scientific data sources. The restoration scaling portion of this NRDA required Trustees to quantify the number of Loggerhead sea turtle hatchlings it would take to replace a post-pelagic juvenile (age 17 to 20 years) and an adult female (42 to 50 years old). To accomplish this, Trustees developed a simple model based on recent life stage and population dynamics assumptions for the south Florida Loggerhead sub-population. Details of the sea turtle NRDA method and rationale for determining the required model input parameters are discussed.


2001 ◽  
Vol 2001 (1) ◽  
pp. 661-665
Author(s):  
Deborah P. French McCay ◽  
Carol-Ann Manen ◽  
Mark Gibson ◽  
John Catena

ABSTRACT The Oil Pollution Act of 1990 (OPA) seeks to make the environment and public whole for injury to or loss of natural resources and services as a result of a discharge of oil. This means that restoration projects implemented as part of a natural resource damage assessment (NRDA) must be of a sufficient scale to produce resources and services of the same type and quality and of comparable value to those that were lost. Services, for an NRDA, include both the ecological and human uses of the resources. Also, the loss must be quantified from the time of impact until the resource returns to baseline conditions—the level in the absence of the impact. This paper details a series of methods that may be used for scaling NRDA restoration projects and describes how these methods were used in the restoring the injuries incurred as a result of the North Cape oil spill.


2005 ◽  
Vol 2005 (1) ◽  
pp. 193-196 ◽  
Author(s):  
M. Irfan Saeed ALRAI ◽  
S.H.N. Rizvi

ABSTRACT The oil tanker Tasman Spirit was grounded in the channel of the port of Karachi, Pakistan on 27, July 2003. The vessel was carrying a cargo of 67,535 tones of Iranian Light crude oil for delivery to the Pakistan Refinery Limited in Karachi when the grounding occurred. Significant quantities of oil were spilled when the Tasman Spirit broke up during the evening of August 13, 2003. By 18 August approximately 27,000 tones of cargo had been lost. The coastal environment in which the Tasman Spirit oil spill (TSOS) occurred is a rich and diverse tropical marine/estuarine ecosystem. It includes extensive mangrove forests, habitat for sea turtles, dolphins, porpoises, and beaked whales, and several species of lizards and sea snakes. The initial findings revealed that the initial impacted area covered about 1600 square kilometer and a coast line of 7.5 kilometer. Pakistan does not have the expertise to deal with oil spill disaster of this magnitude. The rapid assessment report was prepared with the assistance of United Nations Development Programme, United Nations Environment Programme and local experts. The report emphasized the need of carrying out a Natural Resource Damage Assessment (NRDA). This paper highlights important findings of the NRDA study describing the methodologies adapted for the systematic assessment of the extent and severity of the environmental damage and ecological injury resulting from the Tasman Spirit Oil Spill.


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