Oil spill
An oil spill is a release of a liquid petroleum hydrocarbon into the environment due to human activity, and is a form of pollution. The term often refers to marine oil spills, where oil is released into the ocean or coastal waters. Oil spills include releases of crude oil from tankers, offshore platforms, drilling rigs and wells, as well as spills of refined petroleum products (such as gasoline, diesel) and their by-products, and heavier fuels used by large ships such as bunker fuel, or the spill of any oily refuse or waste oil. Spills may take months or even years to clean up.[1]
Oil also enters the marine environment from natural oil seeps.[2] Most human-made oil pollution comes from land-based activity, but public attention and regulation has tended to focus most sharply on seagoing oil tankers.
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Environmental effects
The oil penetrates into the structure of the plumage of birds, reducing its insulating ability, thus making the birds more vulnerable to temperature fluctuations and much less buoyant in the water. It also impairs birds' flight abilities to forage and escape from predators. As they attempt to preen, birds typically ingest oil that covers their feathers, causing kidney damage, altered liver function, and digestive tract irritation. This and the limited foraging ability quickly causes dehydration and metabolic imbalances. Hormonal balance alteration including changes in luteinizing protein can also result in some birds exposed to petroleum.[4]
Most birds affected by an oil spill die unless there is human intervention.[5][6] Marine mammals exposed to oil spills are affected in similar ways as seabirds. Oil coats the fur of Sea otters and seals, reducing its insulation abilities and leading to body temperature fluctuations and hypothermia. Ingestion of the oil causes dehydration and impaired digestions. Because oil floats on top of water, less sunlight penetrates into the water, limiting the photosynthesis of marine plants and phytoplankton. This, as well as decreasing the fauna populations, affects the food chain in the ecosystem. There are three kinds of oil-consuming bacteria. Sulfate-reducing bacteria (SRB) and acid-producing bacteria are anaerobic, while general aerobic bacteria (GAB) are aerobic. These bacteria occur naturally and will act to remove oil from an ecosystem, and their biomass will tend to replace other populations in the food chain.
Cleanup and recovery
Cleanup and recovery from an oil spill is difficult and depends upon many factors, including the type of oil spilled, the temperature of the water (affecting evaporation and biodegradation), and the types of shorelines and beaches involved.[7]
Methods for cleaning up include:
- Bioremediation: use of microorganisms[8] or biological agents[9] to break down or remove oil.
- Bioremediation Accelerator: Oleophilic, hydrophobic chemical, containing no bacteria, which chemically and physically bonds to both soluble and insoluble hydrocarbons. The bioremedation accelerator acts as a herding agent in water and on the surface, floating molecules to the surface of the water, including solubles such as phenols and BTEX, forming gel-like agglomerations. Undetectable levels of hydrocarbons can be obtained in produced water and manageable water columns. By overspraying sheen with bioremediation accelerator, sheen is eliminated within minutes. Whether applied on land or on water, the nutrient-rich emulsion creates a bloom of local, indigenous, pre-existing, hydrocarbon-consuming bacteria. Those specific bacteria break down the hydrocarbons into water and carbon dioxide, with EPA tests showing 98% of alkanes biodegraded in 28 days; and aromatics being biodegraded 200 times faster than in nature they also sometimes use the hydrofireboom to clean the oil up by taking it away from most of the oil and burning it.[10]
- Controlled burning can effectively reduce the amount of oil in water, if done properly.[11] But it can only be done in low wind, and can cause air pollution.[12]
- Dispersants act as detergents, clustering around oil globules and allowing them to be carried away in the water.[13] This improves the surface aesthetically, and mobilizes the oil. Smaller oil droplets, scattered by currents, may cause less harm and may degrade more easily. But the dispersed oil droplets infiltrate into deeper water and can lethally contaminate coral. Recent research indicates that some dispersants are toxic to corals.[14]
- Watch and wait: in some cases, natural attenuation of oil may be most appropriate, due to the invasive nature of facilitated methods of remediation, particularly in ecologically sensitive areas such as wetlands.[15]
- Dredging: for oils dispersed with detergents and other oils denser than water.
- Skimming: Requires calm waters
- Solidifying: Solidifiers are composed of dry hydrophobic polymers that both adsorb and absorb. They clean up oil spills by changing the physical state of spilled oil from liquid to a semi-solid or a rubber-like material that floats on water. Solidifiers are insoluble in water, therefore the removal of the solidified oil is easy and the oil will not leach out. Solidifiers have been proven to be relatively non-toxic to aquatic and wild life and have been proven to suppress harmful vapors commonly associated with hydrocarbons such as Benzene, Xylene, Methyl Ethyl, Acetone and Naphtha. The reaction time for solidification of oil is controlled by the surf area or size of the polymer as well as the viscosity of the oil. Some solidifier product manufactures claim the solidified oil can be disposed of in landfills, recycled as an additive in asphalt or rubber products, or burned as a low ash fuel. A solidifier called C.I.Agent (manufactured by C.I.Agent Solutions of Louisville, Kentucky) is being used by BP in granular form as well as in Marine and Sheen Booms on Dauphin Island, AL and Fort Morgan, MS to aid in the Deepwater Horizon oil spill cleanup.
- Vacuum and centrifuge: oil can be sucked up along with the water, and then a centrifuge can be used to separate the oil from the water - allowing a tanker to be filled with near pure oil. Usually, the water is returned to the sea, making the process more efficient, but allowing small amounts of oil to go back as well. This issue has hampered the use of centrifuges due to a United States regulation limiting the amount of oil in water returned to the sea.[16]
Equipment used includes:[11]
- Booms: large floating barriers that round up oil and lift the oil off the water
- Skimmers: skim the oil
- Sorbents: large absorbents that absorb oil
- Chemical and biological agents: helps to break down the oil
- Vacuums: remove oil from beaches and water surface
- Shovels and other road equipments: typically used to clean up oil on beaches
Prevention
- Seafood Sensory Training- in an effort to detect oil in seafood, inspectors and regulators are being trained to sniff out seafood tainted by oil and make sure the product reaching consumers is safe to eat.[17]
- Secondary containment - methods to prevent releases of oil or hydrocarbons into environment.
- Oil Spill Prevention Containment and Countermeasures (SPCC) program by the United States Environmental Protection Agency.
- Double-hulling - build double hulls into vessels, which reduces the risk and severity of a spill in case of a collision or grounding. Existing single-hull vessels can also be rebuilt to have a double hull.
Environmental Sensitivity Index (ESI) mapping
Environmental Sensitivity Index (ESI) maps are used to identify sensitive shoreline resources prior to an oil spill event in order to set priorities for protection and plan cleanup strategies.[18][19] By planning spill response ahead of time, the impact on the environment can be minimized or prevented. Environmental sensitivity index maps are basically made up of information within the following three categories: shoreline type, and biological and human-use resources.[20]
Shoreline type
Shoreline type is classified by rank depending on how easy the garet would be to cleanup, how long the oil would persist, and how sensitive the shoreline is.[21] The floating oil slicks put the shoreline at particular risk when they eventually come ashore, covering the substrate with oil. The differing substrates between shoreline types vary in their response to oiling, and influence the type of cleanup that will be required to effectively decontaminate the shoreline. In 1995, the US National Oceanic and Atmospheric Administration extended ESI maps to lakes, rivers, and estuary shoreline types.[20] The exposure the shoreline has to wave energy and tides, substrate type, and slope of the shoreline are also taken into account – in addition to biological productivity and sensitivity. The productivity of the shoreline habitat is also taken into account when determining ESI ranking.[22] Mangroves and marshes tend to have higher ESI rankings due to the potentially long-lasting and damaging effects of both the oil contamination and cleanup actions. Impermeable and exposed surfaces with high wave action are ranked lower due to the reflecting waves keeping oil from coming onshore, and the speed at which natural processes will remove the oil.
Biological resources
Habitats of plants and animals that may be at risk from oil spills are referred to as “elements” and are divided by functional group. Further classification divides each element into species groups with similar life histories and behaviors relative to their vulnerability to oil spills. There are eight element groups: Birds, Reptiles Amphibians, Fish, Invertebrates, Habitats and Plants, Wetlands, and Marine Mammals and Terrestrial Mammals. Element groups are further divided into sub-groups, for example, the ‘marine mammals’ element group is divided into dolphins, manatees, pinnipeds (seals, sea lions & walruses), polar bears, sea otters and whales.[20][22] Issues taken into consideration when ranking biological resources include the observance of a large number of individuals in a small area, whether special life stages occur ashore (nesting or molting), and whether there are species present that are threatened, endangered or rare.[23]
Human-use resources
Human use resources are divided into four major classifications; archaeological importance or cultural resource site, high-use recreational areas or shoreline access points, important protected management areas, or resource origins.[20][23] Some examples include airports, diving sites, popular beach sites, marinas, natural reserves or marine sanctuaries.
Estimating the volume of a spill
By observing the thickness of the film of oil and its appearance on the surface of the water, it is possible to estimate the quantity of oil spilled. If the surface area of the spill is also known, the total volume of the oil can be calculated.[24]
| Film thickness | Quantity spread | ||||
|---|---|---|---|---|---|
| Appearance | in | mm | nm | gal/sq mi | L/ha |
| Barely visible | 0.0000015 | 0.0000380 | 38 | 25 | 0.370 |
| Silvery sheen | 0.0000030 | 0.0000760 | 76 | 50 | 0.730 |
| First trace of color | 0.0000060 | 0.0001500 | 150 | 100 | 1.500 |
| Bright bands of color | 0.0000120 | 0.0003000 | 300 | 200 | 2.900 |
| Colors begin to dull | 0.0000400 | 0.0010000 | 1000 | 666 | 9.700 |
| Colors are much darker | 0.0000800 | 0.0020000 | 2000 | 1332 | 19.500 |
Oil spill model systems are used by industry and government to assist in planning and emergency decision making. Of critical importance for the skill of the oil spill model prediction is the adequate description of the wind and current fields. There is a worldwide oil spill modelling (WOSM) program.[25] Tracking the scope of an oil spill may also involve verifying that hydrocarbons collected during an ongoing spill are derived from the active spill or some other source. This can involve sophisticated analytical chemistry focused on finger printing an oil source based on the complex mixture of substances present. Largely, these will be various hydrocarbons, among the most useful being polyaromatic hydrocarbons. In addition, both oxygen and nitrogen heterocyclic hydrocarbons, such as parent and alkyl homologues of carbazole, quinoline, and pyridine, are present in many crude oils. As a result, these compounds have great potential to supplement the existing suite of hydrocarbons targets to fine tune source tracking of petroleum spills. Such analysis can also be used to follow weathering and degradation of crude spills.[26]
Largest oil spills
| Spill / Tanker | Location | Date | *Tons of crude oil | Barrels | US Gallons | References |
|---|---|---|---|---|---|---|
| Kuwaiti oil fires [b] |  Kuwait |
January 1991 - November 1991 | 136,000,000-205,000,000 | 1,000,000,000-1,500,000,000 | 42,000,000,000-63,000,000,000 | [27] |
| Kuwaiti oil lakes [c] | Kuwait |
January 1991 - November 1991 | 3,409,000-6,818,000 | 25,000,000-50,000,000 | 1,050,000,000-2,100,000,000 | [28][29][30] |
| Lakeview Gusher |  United States, Kern County, California |
1910-5-14 – September, 1911 | 1,200,000 | 9,000,000 | 378,000,000 | [31] |
| Gulf War oil spill [d] |  Iraq, Persian Gulf and Kuwait |
1991-1-19 - 1991-1-28 | 818,000–1,091,000 | 6,000,000–8,000,000 | 252,000,000–336,000,000 | [32][33][34] |
| Deepwater Horizon | United States, Gulf of Mexico |
2010-4-20 – 2010-7-15 | 560,000-585,000 | 4,100,000-4,300,000 | 172,000,000-180,000,000 | [35][36][37][38] |
| Ixtoc I |  Mexico, Gulf of Mexico |
1979-6-3 – March 23, 1980 | 454,000–480,000 | 3,329,000–3,520,000 | 139,818,000–147,840,000 | [39][40][41] |
| Atlantic Empress / Aegean Captain |  Trinidad and Tobago |
1979-7-19 | 287,000 | 2,105,000 | 88,396,000 | [42][43][44] |
| Fergana Valley |  Uzbekistan |
1992-3-2 | 285,000 | 2,090,000 | 87,780,000 | [45] |
| Nowruz Field Platform |  Iran, Persian Gulf |
1983-2-4 | 260,000 | 1,907,000 | 80,080,000 | [46] |
| ABT Summer |  Angola, 700 nmi (1,300 km; 810 mi) offshore |
1991-5-28 | 260,000 | 1,907,000 | 80,080,000 | [42] |
| Castillo de Bellver |  South Africa, Saldanha Bay |
1983-8-6 | 252,000 | 1,848,000 | 77,616,000 | [42] |
| Amoco Cadiz |  France, Brittany |
1978-3-16 | 223,000 | 1,635,000 | 68,684,000 | [45][45][42][47][48] |
| MT Haven |  Italy, Mediterranean Sea near Genoa |
1991-4-11 | 144,000 | 1,056,000 | 44,352,000 | [42] |
| Odyssey |  Canada, 700 nmi (1,300 km; 810 mi) off Nova Scotia |
1988-11-10 | 132,000 | 968,000 | 40,656,000 | [42] |
| Sea Star | Iran, Gulf of Oman |
1972-12-19 | 115,000 | 843,000 | 35,420,000 | [45][42] |
| Irenes Serenade |  Greece, Pylos |
1980-02-23 | 100,000 | 733,000 | 30,800,000 | [42] |
| Urquiola |  Spain, A Coruña |
1976-5-12 | 100,000 | 733,000 | 30,800,000 | [42] |
| Torrey Canyon |  United Kingdom, Isles of Scilly |
1967-3-18 | 80,000–119,000 | 587,000–873,000 | 24,654,000–36,666,000 | [45][42] |
| Greenpoint Oil Spill | United States, Brooklyn, New York City |
1940–1950s | 55,000– 97,000 | 400,000–710,000 | 17,000,000–30,000,000 | [49] |
a One ton of crude oil is roughly equal to 308 US gallons or 7.33 barrels approx.; 1 oil barrel is equal to 35 imperial or 42 US gallons.
b Estimates for the amount of oil burned in the Kuwaiti oil fires range from 500,000,000 to nearly 2,000,000,000 barrels. 732 wells were set ablaze, while many others were severely damaged and gushed uncontrolled for several months. The fires alone were estimated to consume approximately 6,000,000 barrels of oil per day at their peak. However, it is difficult to find reliable sources for the total amount of oil burned. The range of 1 to 1.5 billion barrels given here represents frequently-cited figures, but better sources are needed.
c Oil spilled from sabotaged fields in Kuwait during the 1991 Persian Gulf War pooled in approximately 300 oil lakes, estimated by the Kuwaiti Oil Minister to contain approximately 25,000,000 to 50,000,000 barrels of oil. According to the U.S. Geological Survey, this figure does not include the amount of oil absorbed by the ground, forming a layer of "tarcrete" over approximately five percent of the surface of Kuwait, fifty times the area occupied by the oil lakes.[50]
d Estimates for the Gulf War oil spill range from 4,000,000 to 11,000,000 barrels. The figure of 6,000,000 to 8,000,000 barrels is the range adopted by the U.S. Environmental Protection Agency and the United Nations in the immediate aftermath of the war, 1991-1993, and is still current, as cited by NOAA and The New York Times in 2010.[51] This amount only includes oil discharged directly into the Persian Gulf by the retreating Iraqi forces from January 19 to 28, 1991. However, according to the U.N. report, oil from other sources not included in the official estimates continued to pour into the Persian Gulf through June, 1991. The amount of this oil was estimated to be at least several hundred thousand barrels, and may have factored into the estimates above 8,000,000 barrels.
See also
- Environmental issues with petroleum
- Environmental issues with shipping
- List of oil spills
- LNG spill
- Low-temperature thermal desorption
- National Oil and Hazardous Substances Pollution Contingency Plan
- Ohmsett (Oil and Hazardous Materials Simulated Environmental Test Tank)
- Oil Pollution Act of 1990 (in the US)
- Oil well
- Penguin sweater
- Project Deep Spill, the first intentional deepwater oil and gas spill
- Pseudomonas putida (used for degrading oil)
- S-200 (fertilizer)
- Spill containment
- Tarball
References
- ↑ "Hindsight and Foresight, 20 Years After the Exxon Valdez Spill". NOAA. 2010-03-16. http://vimeo.com/10216588. Retrieved 2010-04-30.
- ↑ http://seeps.geol.ucsb.edu/
- ↑ "Less Than 1% of Oil-Soaked Birds Survive : TreeHugger". www.treehugger.com. http://www.treehugger.com/files/2010/06/less-1-percent-oil-soaked-birds-survive.php. Retrieved 2010-06-09.
- ↑ C. Michael Hogan (2008), "Magellanic Penguin", GlobalTwitcher.com, ed. N. Stromberg.
- ↑ Dunnet, G., Crisp, D., Conan, G., Bourne, W. (1982) "Oil Pollution and Seabird Populations [and Discussion]" Philosophical Transactions of the Royal Society of London. B 297(1087): 413–427
- ↑ Untold Seabird Mortality due to Marine Oil Pollution, Elements Online Environmental Magazine.
- ↑ Lingering Lessons of the Exxon Valdez Oil Spill
- ↑ "The Environmental Literacy Council - Oil Spills". Enviroliteracy.org. 2008-06-25. http://www.enviroliteracy.org/article.php/540.html. Retrieved 2010-06-16.
- ↑ "Biological Agents". http://www.epa.gov/osweroe1/content/learning/bioagnts.htm.
- ↑ "S-200 | NCP Product Schedule | Emergency Management | US EPA". Epa.gov. http://www.epa.gov/emergencies/content/ncp/products/s200.htm. Retrieved 2010-06-16.
- ↑ 11.0 11.1 "Emergency Response: Responding to Oil Spills". Office of Response and Restoration. National Oceanic and Atmospheric Administration. 2007-06-20. http://response.restoration.noaa.gov/topic_subtopic_entry.php?RECORD_KEY(entry_subtopic_topic)=entry_id,subtopic_id,topic_id&entry_id(entry_subtopic_topic)=184&subtopic_id(entry_subtopic_topic)=8&topic_id(entry_subtopic_topic)=1.
- ↑ Oil Spills
- ↑ "Detergent and Oil Spills". NEWTON BBS. 2002-10-12. http://www.newton.dep.anl.gov/askasci/chem00/chem00896.htm. Retrieved 2007-07-29.
- ↑ Barry, Carolyn (2007). Slick Death: Oil-spill treatment kills coral, Science News vol. 172, p. 67.
- ↑ Pezeshki, S. R., Hester, M. W., Lin, Q. & Nyman, J. A. (2000). The effects of oil spill clean-up on dominant US Gulf coast marsh macrophytes: a review. Environmental Pollution. 108: 129-139.
- ↑ Fountain, Henry (2010-06-24). "Advances in Oil Spill Cleanup Lag Since Valdez". New York Times. http://www.nytimes.com/2010/06/25/us/25clean.html. Retrieved 2010-07-05.
- ↑ "Trained noses to sniff out Gulf seafood for oil - Yahoo! News". News.yahoo.com. 2010-06-07. http://news.yahoo.com/s/ap/20100607/ap_on_bi_ge/us_gulf_oil_spill_seafood_sniffers. Retrieved 2010-06-16.
- ↑ "Environmental Sensitivity Index (ESI) Maps". http://response.restoration.noaa.gov/resource_resourcetopic.php?RECORD_KEY(resourcetopics)=resourcetopic_id&resourcetopic_id(resourcetopics)=37. Retrieved 2010-05-27.
- ↑ "NOAA's Ocean Service Office of Response and Restoration". Response.restoration.noaa.gov. http://response.restoration.noaa.gov/. Retrieved 2010-06-16.
- ↑ 20.0 20.1 20.2 20.3 NOAA (2002). Environmental Sensitivity Index Guidelines, version 3.0. NOAA Technical Memorandum NOS OR&R 11. Seattle: Hazardous Response and Assessment Division, National Oceanic and Atmospheric Administration, 129p.
- ↑ Gundlach, E.R. and M.O. Hayes (1978). Vulnerability of Coastal Environments to Oil Spill Impacts. Marine Technology Society. 12 (4): 18-27.
- ↑ 22.0 22.1 NOAA (2008). Introduction to Environmental Sensitivity Index maps. NOAA Technical Manual. Seattle: Hazardous Response and Assessment Division, National Oceanic and Atmospheric Administration, 56p.
- ↑ 23.0 23.1 IMO/IPIECA (1994). Sensitivity Mapping for Oil Spill Response. International Maritime Organization/ International Petroleum Industry Environmental Conservation Association Report Series, Volume 1. 22p.
- ↑ Metcalf & Eddy. Wastewater Engineering, Treatment and Reuse. 4th ed. New York: McGraw-Hill, 2003. 98.
- ↑ Anderson, E.L., E. Howlett, K. Jayko, V. Kolluru, M. Reed, and M. Spaulding. 1993. The worldwide oil spill model (WOSM): an overview. Pp. 627–646 in Proceedings of the 16th Arctic and Marine Oil Spill Program, Technical Seminar. Ottawa, Ontario: Environment Canada.
- ↑ Wang, Z., M. Fingas, and D.S. Page. 1999. Oil spill identification. Journal of Chromatography A. 843: 369-411. doi:10.1016/S0021-9673(99)00120-X.
- ↑ CNN.com, Kuwait still recovering from Gulf War fires, 3 Jan. 2003.
- ↑ United Nations, Updated Scientific Report on the Environmental Effects of the Conflict between Iraq and Kuwait, 8 Mar. 1993.
- ↑ United States Geological Survey, Campbell, Robert Wellman, ed. 1999. Iraq and Kuwait: 1972, 1990, 1991, 1997. Earthshots: Satellite Images of Environmental Change. U.S. Geological Survey. http://earthshots.usgs.gov, revised 14 Feb. 1999.
- ↑ National Aeronautics and Space Administration, Goddard Space Flight Center News, 1991 Kuwait Oil Fires, 21 Mar. 2003.
- ↑ "California's legendary oil spill". Los Angeles Times. 2010-06-13. http://articles.latimes.com/2010/jun/13/local/la-me-then-20100613. Retrieved 2010-07-14.
- ↑ United States Environmental Protection Agency, Report To Congress United States Gulf Environmental Technical Assistance From January 27 - July 31 1991
- ↑ United Nations, Updated Scientific Report on the Environmental Effects of the Conflict between Iraq and Kuwait, 8 Mar. 1993.
- ↑ National Oceanic and Atmospheric Administration, Office of Response and Restoration, Emergency Response Division, Incident News: Arabian Gulf Spills, updated 18 May 2010.
- ↑ Campbell Robertson /Clifford Krauss (2 August 2010). "Gulf Spill Is the Largest of Its Kind, Scientists Say". New York Times. http://www.nytimes.com/2010/08/03/us/03spill.html?_r=1&hp. Retrieved 2 August 2010.
- ↑ CNN (1 July 2010). "Oil disaster by the numbers". CNN. http://www.cnn.com/SPECIALS/2010/gulf.coast.oil.spill/interactive/numbers.interactive/index.html. Retrieved 1 July 2010.
- ↑ Consumer Energy Report (20 June 2010). "Internal Documents: BP Estimates Oil Spill Rate up to 100,000 Barrels Per Day". Consumer Energy Report. http://www.consumerenergyreport.com/2010/06/20/internal-document-bp-estimates-spill-rate-up-to-100000-bpd/. Retrieved 20 June 2010.
- ↑ Big Oil Plans Rapid Response to Future Spills
- ↑ "IXTOC I". National Oceanic and Atmospheric Administration. http://www.incidentnews.gov/incident/6250. Retrieved 2008-11-03.
- ↑ "Ixtoc 1 oil spill: flaking of surface mousse in the Gulf of Mexico". Nature Publishing Group. http://www.nature.com/nature/journal/v290/n5803/abs/290235a0.html. Retrieved 2008-11-03.
- ↑ John S. Patton, Mark W. Rigler, Paul D. Boehm & David L. Fiest (1981-03-19). "Ixtoc 1 oil spill: flaking of surface mousse in the Gulf of Mexico". NPG (Nature Publishing Group). http://www.nature.com/nature/journal/v290/n5803/abs/290235a0.html. Retrieved 2007-07-29.
- ↑ 42.0 42.1 42.2 42.3 42.4 42.5 42.6 42.7 42.8 42.9 "Major Oil Spills". International Tanker Owners Pollution Federation. http://www.itopf.com/stats.html. Retrieved 2008-11-02.
- ↑ "Atlantic Empress". Centre de Documentation de Recherche et d'Expérimentations. http://www.cedre.fr/uk/spill/atlantic/atlantic.htm. Retrieved 2008-11-10.
- ↑ "Tanker Incidents". http://www.maritime-connector.com/ContentDetails/1479/gcgid/193/lang/English/Tanker-Incidents.wshtml. Retrieved 2009-07-19.
- ↑ 45.0 45.1 45.2 45.3 45.4 "Oil Spill History". The Mariner Group. http://www.marinergroup.com/oil-spill-history.htm. Retrieved 2008-11-02.
- ↑ "Oil Spills and Disasters". http://www.infoplease.com/ipa/A0001451.html. Retrieved 2008-11-16.
- ↑ "Amoco Cadiz". National Oceanic and Atmospheric Administration. http://www.incidentnews.gov/incident/6241. Retrieved 2008-11-16.
- ↑ [1]
- ↑ "An Oil Spill Grows in Brooklyn". New York Times. 2010-05-14. http://www.nytimes.com/2010/05/16/opinion/16Prudhomme.html. Retrieved 2010-07-18.
- ↑ United States Geological Survey, Campbell, Robert Wellman, ed. 1999. Iraq and Kuwait: 1972, 1990, 1991, 1997. Earthshots: Satellite Images of Environmental Change. U.S. Geological Survey. http://earthshots.usgs.gov, revised 14 Feb. 1999.
- ↑ Gulf Oil Spill Is Bad, but How Bad?, last updated 20 May, 2010.
Further reading
- The World Almanac and Book of Facts, 2004
- Oil Spill Case Histories 1967-1991, NOAA/Hazardous Materials and Response Division, Seattle WA, 1992
- Nelson-Smith, Oil Pollution and Marine Ecology, Elek Scientific, London, 1972; Plenum, New York, 1973
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