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Oil spill
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An oil spill is the 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. The oil may be a variety of materials, including crude oil, refined petroleum products (such as gasoline or diesel fuel) or by-products, ships' bunkers, oily refuse or oil mixed in waste. Spills take months or even years to clean up.
Oil is also released into the environment from natural geologic seeps on the sea floor.

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An oil spill is the 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. The oil may be a variety of materials, including crude oil, refined petroleum products (such as gasoline or diesel fuel) or by-products, ships' bunkers, oily refuse or oil mixed in waste. Spills take months or even years to clean up.
Oil is also released into the environment from natural geologic seeps on the sea floor. 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.
Environmental effects The oil penetrates and opens up the structure of the plumage of birds, reducing its insulating ability, and so making the birds more vulnerable to temperature fluctuations and much less buoyant in the water. It also impairs birds' flight abilities, making it difficult or impossible to forage and escape from predators. As they attempt to preen, birds typically ingest oil that coats 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. Most birds affected by an oil spill die unless there is human intervention.
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.
Methods of cleaning
A sheen is usually dispersed (but not cleaned up) with detergents which makes oil settle to the bottom. Oils that are denser than water, such as Polychlorinated biphenyls (PCBs), can be more difficult to clean as they make the seabed toxic.
Methods for cleaning up include:
- Bioremediation: use of microorganisms or biological agents 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. Non-detectable levels of hydrocarbons can be obtained in produced water and manageable water columns. By overspraying sheen with bioremediation accelerator, sheen is elimiinated within minutes. Whether applied on land or on water, the nutrient-rich, create a bloom of local, indigenous, pre-existing, hydrocarbon-consuming bacteria, which break down the hydrocarbons into water and carbon dioxide.
- Controlled burning can effectively reduce the amount of oil in water, if done properly. But it can only be done in low wind, and can cause air pollution.
- Dispersants act as detergents, clustering around oil globules and allowing them to be carried away in the water. 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.
- Watch and wait: in some cases, nautural attentuation of oil may be most appropriate, due to the invasive nature of facilitated methods of remediation, particularly in ecologically sensitive areas.
- Dredging: for oils dispersed with detergents and other oils denser than water.
- Skimming: Requires calm waters
- Solidifying
Equipment used includes:
- 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
- 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.
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.
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.
| Film thickness | Quantity spread |
|---|
| Appearance | in | mm | gal/sq mi | L/ha |
|---|
| Barely visible | 0.0000015 | 0.0000380 | 25 | 0.370 | | Silvery sheen | 0.0000030 | 0.0000760 | 50 | 0.730 | | First trace of color | 0.0000060 | 0.0001500 | 100 | 1.500 | | Bright bands of color | 0.0000120 | 0.0003000 | 200 | 2.900 | | Colors begin to dull | 0.0000400 | 0.0010000 | 666 | 9.700 | | Colors are much darker | 0.0000800 | 0.0020000 | 1332 | 19.500 |
Largest oil spills
Oil spills of over 100,000 tons or 30 million US gallons, ordered by tons| Spill / Tanker | Location | Date | *Tons of crude oil | Reference | | Gulf War oil spill | Persian Gulf | January 23, 1991 | 136,000 - 1,500,000 | | | Ixtoc I oil well | Gulf of Mexico | June 3, 1979–March 23, 1980 | 454,000 - 480,000 | | | Atlantic Empress / Aegean Captain | Trinidad and Tobago | July 19, 1979 | 287,000 | | | Fergana Valley | Uzbekistan | March 2, 1992 | 285,000 | | | Nowruz oil field | Persian Gulf | February 1983 | 260,000 | | | ABT Summer | Angola | 1991 | 260,000 | | | Castillo de Bellver | Saldanha Bay, South Africa | August 6, 1983 | 252,000 | | | Amoco Cadiz | Brittany, France | March 16, 1978 | 223,000 | | | Amoco Haven tanker disaster | Mediterranean Sea near Genoa, Italy | 1991 | 144,000 | | | Odyssey | Nova Scotia, Canada | 1988 | 132,000 | | | Sea Star | Gulf of Oman | December 19, 1972 | 115,000 | | | Torrey Canyon | Scilly Isles, UK | March 18, 1967 | 80,000 - 119,000 | | | Irenes Serenade | Navarino Bay, Greece | 1980 | 100,000 | | | Urquiola | A Coruña, Spain | May 12, 1976 | 100,000 | |
One tonne of crude oil is roughly equal to 308 US gallons, or 7.33 barrels.
See also
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
External links
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