The Cost of Oil Spills from Tankers in Relation to Weight of Spilled Oil

2009 ◽  
Vol 46 (04) ◽  
pp. 219-228
Author(s):  
Yashuhira Yamada

The purpose of this paper is to consider a practical way to estimate the cost of oil spills from ships within the framework of establishing environmental risk evaluation criteria in International Maritime Organization (IMO). Regression analysis between the cost of oil spills and the weight of oil spilled (oil spill weight) was carried out using historical oil spill data from tankers reported by International Oil Pollution Compensation (IOPC) Funds. A nonlinear regression formula between the cost of oil spills and the oil spill weight is estimated from the historical data, and a critical value of cost to avert one tonne of spilled oil (CATScr) is obtained. CATScr obtained by the present study is compared with that obtained by previous work. This study shows that the cost of oil spills estimated by the present regression formula is in fairly good agreement with the mean value obtained from historical data while the CATScr gives relatively larger costs and shows the upper bound of the cost of oil spills.

1999 ◽  
Vol 1999 (1) ◽  
pp. 257-265
Author(s):  
Edward J. Maillett ◽  
Gary A. Yoshioka

ABSTRACT The purpose of this paper is to estimate the cumulative cost incurred by private industry as a result of the various regulations enacted under the Oil Pollution Act of 1990 (OPA 90) and to compare these costs against the estimated effectiveness of the program in terms of avoided future oil spills. The authors reviewed Federal Register announcements of federal agency rulemakings to identify estimated costs to industry and to determine if reported costs are one-time occurrences for capital-related expenditures or represent annual estimates for repeated activities. The authors then estimated the total costs of each rulemaking through the year 2015. The costs of regulations implemented under OPA 90 that impact the private sector range from zero to $3.5 billion in discounted dollars. Based on these individual government estimates for each OPA 90 regulation, the authors estimate the discounted cost to industry to comply with all of the OPA 90 requirements to be $12.1 billion, the largest portion of which affects the marine vessel industry. Total benefits of the rulemakings are estimated to exceed 3.6 million barrels of avoided oil spills through the year 2015. Over one-half of this benefit estimate results from the facility response planning requirements for non-transportation-related on-shore facilities and pipelines. The cost effectiveness of regulations implemented under OPA 90 ranges between several hundred dollars to over $26,000 per barrel of avoided oil spill.


2005 ◽  
Vol 2005 (1) ◽  
pp. 439-442 ◽  
Author(s):  
Charlie Henry

ABSTRACT Since the Oil Pollution Act of 1990 (OPA 90), dispersants have been used as part of a combined response to mitigate seven oil spills in United States Gulf of Mexico (GOM) waters. Of the dispersant operations reported, four utilized the Regional Response Team VI pre-approval authority to the Federal On-Scene Coordinator (FOSC) that requires a monitoring plan. The successful integration of dispersant pre-authorization along with a fully funded ready response delivery system maintained by industry contributed to the successful use of dispersants to aid in mitigating spilled oil. A key element to gaining the original pre-approval authority was a functional operational monitoring plan. While each response was considered a successful dispersant operation, each incident provided valuable lessons learned that have been integrated into subsequent contingency planning and modifications to existing pre-authorization requirements in the GOM. This paper provides a chronological review of oil spill responses where dispersants were applied in the GOM since OPA 90.


1999 ◽  
Vol 1999 (1) ◽  
pp. 41-47 ◽  
Author(s):  
Catherine J. Grey

ABSTRACT The 1971 and 1992 International Oil Pollution Compensation Funds (IOPC Funds) provide compensation to the victims of oil spills from tankers in countries which have ratified the 1971 and 1992 Fund Conventions. Since 1978, they have dealt with more than 100 incidents, paying compensation in 68 of these. Details of the individual incidents are given together with the total cost for each, expressed in US$. The numbers, sizes and costs of the incidents are analysed in detail and compared with the incidence of all tanker spills in Fund countries, using data from the International Tanker Owners Pollution Federation's (ITOPF) Oil Spill Database. This analysis reveals a number of trends relating to the size of tankers; the amount and type of oil spilled; and the geographical location. The 1971 IOPC Fund has undoubtedly proved highly effective, but recent incidents have tested the limits of compensation available. The 1992 Fund Convention entered into force in May 1996, providing both higher limits and a broader scope. However, the threshold at which it comes into effect is also higher, thereby excluding many of the less expensive spills which would previously have been covered by the 1971 Fund Convention. The significance of this for the numbers and costs of incidents likely to be dealt with by both the 1971 and the 1992 IOPC Funds is examined.


1969 ◽  
Vol 1969 (1) ◽  
pp. 151-156
Author(s):  
J. Stephen Dorrler

Abstract When compared on an individual basis to major oil pollution disasters, the average Navy oil spillage incident seems insignificant. However, when the cleanup costs are tallied, these limited oil spills do not appear so small. For example, a one barrel oil spill, discharged from a destroyer berthed at the Long Beach Naval Shipyard, took nine laborers, a boat operator, a truck driver, a crane operator and a supervisor one and a half days to clean up at a cost of $1,300. On the East Coast, the Norfolk Naval Shipyard spends approximately $1,000 an incident in its oil spill cleanup operations. These spills vary between 50 and 500 gallons. From the presented data which defines the limited oil spill, three general statements are derived:1. Limited oil spills are a large problem due to their numerous occurrences.2. Limited oil spills require proper treatment.3. Limited oil spills are expensive to treat. This paper investigates this last statement and by so doing discloses the actual problems which contribute to the high cost of cleaning up limited oil spills. Three factors are discussed:1. The physical conditions affecting an oil spill.,a. Location of the slick,b. Oil Slick Movement,(1) Spreading,(2) Weather, wind and current effects,2. The type of equipment employed.,a. Booms,b. Chemical Dispersants,c. Physical Removal,(1) Skimmers,(2) Straws,3. The completeness of the removal operation. The limited harbor oil spill is expensive and the cost is expected to rise. At the present time, the typical oil spill costs the Navy over $1,000 to clean up. This cost will increase as control agencies rightfully require more removal and more complete removal.


1991 ◽  
Vol 1991 (1) ◽  
pp. 377-383
Author(s):  
Richard W. Dunford ◽  
Sara P. Hudson ◽  
William H. Desvousges

ABSTRACT The new Oil Pollution Act of 1990 defines natural resource damages from oil spills as the sum of the cost to restore foregone natural resource services, the diminution of value of natural resource services prior to restoration, and damage assessment costs. Natural resource damages are usually determined once removal activities (containment, protection, and cleanup) are completed. Nevertheless, removal activities affect the magnitude of all three natural resource damage components. Consequently, to minimize the total cost of oil spills, decisions on removal activities should consider the linkages between removal activities and natural resource damages. Successful containment results in minimal natural resource damages, because oil generally does far less damage to natural resources in open water than on shore. If oil cannot be contained, the potential natural resource damages from oil coming ashore in certain areas can help determine priorities for protection activities. In particular, oil may harm natural resource services much more in some areas than in others. Furthermore, some natural resource services are more costly to restore and assess than others. Finally, some cleanup activities do more harm than good to natural resource services. If the effects of cleanup activities on natural resource damages are ignored, “excessive” cleanup activities are likely.


Author(s):  
Emilio D’Ugo ◽  
Milena Bruno ◽  
Arghya Mukherjee ◽  
Dhrubajyoti Chattopadhyay ◽  
Roberto Giuseppetti ◽  
...  

AbstractMicrobiomes of freshwater basins intended for human use remain poorly studied, with very little known about the microbial response to in situ oil spills. Lake Pertusillo is an artificial freshwater reservoir in Basilicata, Italy, and serves as the primary source of drinking water for more than one and a half million people in the region. Notably, it is located in close proximity to one of the largest oil extraction plants in Europe. The lake suffered a major oil spill in 2017, where approximately 400 tons of crude oil spilled into the lake; importantly, the pollution event provided a rare opportunity to study how the lacustrine microbiome responds to petroleum hydrocarbon contamination. Water samples were collected from Lake Pertusillo 10 months prior to and 3 months after the accident. The presence of hydrocarbons was verified and the taxonomic and functional aspects of the lake microbiome were assessed. The analysis revealed specialized successional patterns of lake microbial communities that were potentially capable of degrading complex, recalcitrant hydrocarbons, including aromatic, chloroaromatic, nitroaromatic, and sulfur containing aromatic hydrocarbons. Our findings indicated that changes in the freshwater microbial community were associated with the oil pollution event, where microbial patterns identified in the lacustrine microbiome 3 months after the oil spill were representative of its hydrocarbonoclastic potential and may serve as effective proxies for lacustrine oil pollution.


2012 ◽  
Vol 11 (1-2) ◽  
pp. 100
Author(s):  
C. E. Stringari ◽  
W. C. Marques ◽  
L. F. Mello ◽  
R. T. Edit

Oil spills can generate different effects in different time scales on the marine ecosystem. The numerical modeling of this process is an important tool with low computational cost which provides a powerful appliance to environmental agencies regarding the risk management. In this way, the objective of this work is evaluate the local wind influence in a hypothetical oil spill along the Southern Brazilian shelf. The numerical simulation was carried using the ECOS model (Easy Coupling Oil System), an oil spill model developed at the Universidade Federal do Rio Grande – FURG, coupled with the tridimensional hydrodynamical model TELEMAC3D (EDF, France). The hydrodynamic model provides the velocities, salinity and temperature fields used by the oil spill model to evaluate the behavior and fate of the oil. The results suggest that the local wind influence are the main forcing driven the fate of the spilled oil. The direction and intensity of the currents are important controlling the behavior and the tridimensional transportation of the oil, on the other hand, the turbulent diffusion is important for the horizontal drift of the oil. The weathering results indicate 40% of evaporation and 80% of emulsification, and the combination of these processes leads an increasing of the oil density around 53.4 kg/m³ after 5 days of simulation.


2020 ◽  
Vol 8 (2) ◽  
pp. 69 ◽  
Author(s):  
Kwang-Ho Lee ◽  
Tag-Gyeom Kim ◽  
Yong-Hwan Cho

The purpose of this study is to investigate the effects of three external forces (tidal current, wind, and waves) on the movement of oil spilled during the Hebei Spirit oil spill accident. The diffusion of the spilled oil was simulated by using a random walk (RW) model that tracks the movement caused by advection-diffusion assuming oil as particles. For oil simulation, the wind drift current generated by wind and tidal current fields were computed by using the environmental fluid dynamics code (EFDC) model. Next, the wave fields were simulated by using the simulating waves nearshore (SWAN) model, and the Stokes drift current fields were calculated by applying the equation proposed by Stokes. The computed tidal currents, wind drift currents, and Stokes drift currents were applied as input data to the RW model. Then, oil diffusion distribution for each external force component was investigated and compared with that obtained from satellite images. When the wind drift currents and Stokes drift currents caused by waves were considered, the diffusion distribution of the spilled oil showed good agreement with that obtained from the observation.


2019 ◽  
Vol 7 (7) ◽  
pp. 216 ◽  
Author(s):  
Anatoly Shavykin ◽  
Andrey Karnatov

Preparedness for oil spill response is a challenge for many coastal countries. Responders are unable to take effective action unless maps that indicate areas with different vulnerability to oil pollution are available. Such maps, developed in many countries, are usually based on calculations with rank (ordinal) values. However, arithmetic operations with them cannot be allowed. The article describes a method of constructing maps using metric values. The calculations take into account the biomass and the quantity of important biota components, especially significant socio-economic objects and protected areas. The biota distribution densities are represented in the identical units. The vulnerability factors are assessed based on the potential impact of spilled oil on biota, as well as its sensitivity and recoverability after disturbance. The proposed method takes into account the different sensitivity of biota inhabiting in the water column and on the sea surface. Oil vulnerability maps for Kola Bay using the proposed algorithm are presented.


1978 ◽  
Vol 35 (5) ◽  
pp. 510-520 ◽  
Author(s):  
John M. Teal ◽  
Kathryn Burns ◽  
John Farrington

We have analyzed the two- and three-ring aromatic hydrocarbons from the Wild Harbor oil spill in September 1969 and the Winsor Cove oil spill in October 1974, in intertidal marsh sediments, using glass capillary gas-chromatographic and mass-fragmentographic analyses. Naphthalenes with 0–3 alkyl substitutions and phenanthrenes with 0–2 substitutions decreased in concentration with time in surface sediments. The more substituted aromatics decreased relatively less and in some cases actually increased in absolute concentration. The changes in composition of the aromatic fraction have potential consequences for the ecosystem and provide insight into geochemical processes of oil weathering. Key words: oil pollution, aromatic hydrocarbons; gas chromatography; gas chromatography–mass spectrometry; geochemistry; marsh; sediments; oil spills


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