An oil spill is the release of a liquid petroleum hydrocarbon into the environment, especially the marine ecosystem, due to human activity, and is a form of pollution. The term is usually given to marine oil spills, where oil is released into the ocean or coastal waters, but spills may also occur on land. Oil spills may be due to 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, heavier fuels used by large ships such as bunker fuel, or the spill of any oily refuse or waste oil.
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Oil spills penetrate into the structure of the plumage of birds and the fur of mammals, reducing its insulating ability, and making them more vulnerable to temperature fluctuations and much less buoyant in the water. 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. Spills may take weeks, months or even years to clean up.
Oil spills can have disastrous consequences for society; economically, environmentally, and socially. As a result, oil spill accidents have initiated intense media attention and political uproar, bringing many together in a political struggle concerning government response to oil spills and what actions can best prevent them from happening.
Largest oil spills
Crude oil and refined fuel spills from tanker ship accidents have damaged vulnerable ecosystems in Alaska, the Gulf of Mexico, the Galapagos Islands, France, the Sundarbans, Ogoniland, and many other places. The quantity of oil spilled during accidents has ranged from a few hundred tons to several hundred thousand tons (e.g., Deepwater Horizon Oil Spill, Atlantic Empress, Amoco Cadiz), but volume is a limited measure of damage or impact. Smaller spills have already proven to have a great impact on ecosystems, such as the Exxon Valdez oil spill because of the remoteness of the site or the difficulty of an emergency environmental response.
Since 2004, between 300 and 700 barrels of oil per day have been leaking from the site of an oil-production platform 12 miles off the Louisiana coast which sank in the aftermath of Hurricane Ivan. The oil spill, which officials estimate could continue throughout the 21st century, will eventually overtake the 2010 BP Deepwater Horizon disaster as the largest ever, but there are currently no efforts to cap the many leaking well heads.
Oil spills at sea are generally much more damaging than those on land, since they can spread for hundreds of nautical miles in a thin oil slick which can cover beaches with a thin coating of oil. These can kill seabirds, mammals, shellfish and other organisms they coat. Oil spills on land are more readily containable if a makeshift earth dam can be rapidly bulldozed around the spill site before most of the oil escapes, and land animals can avoid the oil more easily.
|Spill / Tanker||Location||Date||Tonnes of crude oil|
|Kuwaiti Oil Fires||Kuwait||January 16, 1991 – November 6, 1991||136,000||1,000,000||42,000,000|
|Kuwaiti Oil Lakes||Kuwait||January 1991 – November 1991||3,409–6,818||25,000–50,000||1,050,000–2,100,000|
|Lakeview Gusher||Kern County, California, USA||March 14, 1910 – September 1911||1,200||9,000||378,000|
|Gulf War oil spill||Kuwait, Iraq, and the Persian Gulf||January 19, 1991 – January 28, 1991||818–1,091||6,000–8,000||252,000–336,000|
|Deepwater Horizon||United States, Gulf of Mexico||April 20, 2010 – July 15, 2010||560–585||4,100–4,900||189,000–231,000|
|Ixtoc I||Mexico, Gulf of Mexico||June 3, 1979 – March 23, 1980||454–480||3,329–3,520||139,818–147,840|
|Atlantic Empress / Aegean Captain||Trinidad and Tobago||July 19, 1979||287||2,105||88,396|
|Fergana Valley||Uzbekistan||March 2, 1992||285||2,090||87,780|
|Nowruz Field Platform||Iran, Persian Gulf||February 4, 1983||260||1,900||80,000|
|ABT Summer||Angola, 700 nmi (1,300 km; 810 mi) offshore||May 28, 1991||260||1,907||80,080|
|Castillo de Bellver||South Africa, Saldanha Bay||August 6, 1983||252||1,848||77,616|
|Amoco Cadiz||France, Brittany||March 16, 1978||223||1,635||68,684|
|Taylor Energy||United States, Gulf of Mexico||September 23, 2004 – Present||210–490||1,500–3,500||63,000–147,000|
|Odyssey||off the coast of Nova Scotia, Canada||November 10, 1988||132||968||40,704|
|Torrey Canyon||England, Cornwall||March 18, 1967||119||872||36,635|
- One metric ton (tonne) of crude oil is roughly equal to 308 US gallons or 7.33 barrels approx.; 1 oil barrel (bbl) is equal to 35 imperial or 42 US gallons. Approximate conversion factors. Archived 2014-06-21 at the Wayback Machine
- Estimates for the amount of oil burned in the Kuwaiti Oil Fires range from 500,000,000 barrels (79,000,000 m3) to nearly 2,000,000,000 barrels (320,000,000 m3). Between 605 and 732 wells were set ablaze, while many others were severely damaged and gushed uncontrolled for several months. It took over ten months to bring all of the wells under control. The fires alone were estimated to consume approximately 6,000,000 barrels (950,000 m3) of oil per day at their peak.
- 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 (7,900,000 m3) 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.
- Estimates for the Gulf War oil spill range from 4,000,000 to 11,000,000 barrels (1,700,000 m3). The figure of 6,000,000 to 8,000,000 barrels (1,300,000 m3) 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. 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 (1,300,000 m3).
An oil spill represents an immediate fire hazard. The Kuwaiti oil fires produced air pollution that caused respiratory distress. The Deepwater Horizon explosion killed eleven oil rig workers. The fire resulting from the Lac-Mégantic derailment killed 47 and destroyed half of the town's centre.
Spilled oil can also contaminate drinking water supplies. For example, in 2013 two different oil spills contaminated water supplies for 300,000 in Miri, Malaysia; 80,000 people in Coca, Ecuador. In 2000, springs were contaminated by an oil spill in Clark County, Kentucky.
Contamination can have an economic impact on tourism and marine resource extraction industries. For example, the Deepwater Horizon oil spill impacted beach tourism and fishing along the Gulf Coast, and the responsible parties were required to compensate economic victims.
The threat posed to birds, fish, shellfish and crustaceans from spilled oil was known in England in the 1920s, largely through observations made in Yorkshire. The subject was also explored in a scientific paper produced by the National Academy of Sciences in the US in 1974 which considered impacts to fish, crustaceans and molluscs. The paper was limited to 100 copies and was described as a draft document, not to be cited.
In general, spilled oil can affect animals and plants in two ways: dirесt from the oil and from the response or cleanup process. There is no clear relationship between the amount of oil in the aquatic environment and the likely impact on biodiversity. A smaller spill at the wrong time/wrong season and in a sensitive environment may prove much more harmful than a larger spill at another time of the year in another or even the same environment. Oil penetrates into the structure of the plumage of birds and the fur of mammals, reducing their insulating ability, and making them more vulnerable to temperature fluctuations and much less buoyant in the water.
Animals who rely on scent to find their babies or mothers cannot due to the strong scent of the oil. This causes a baby to be rejected and abandoned, leaving the babies to starve and eventually die. Oil can impair a bird's ability to fly, preventing it from foraging or escaping from predators. As they preen, birds may ingest the oil coating their feathers, irritating the digestive tract, altering liver function, and causing kidney damage. Together with their diminished foraging capacity, this can rapidly result in dehydration and metabolic imbalance. Some birds exposed to petroleum also experience changes in their hormonal balance, including changes in their luteinizing protein. The majority of birds affected by oil spills die from complications without human intervention. Some studies have suggested that less than one percent of oil-soaked birds survive, even after cleaning, although the survival rate can also exceed ninety percent, as in the case of the MV Treasure oil spill. Oil spills and oil dumping events have been impacting sea birds since at least the 1920s and was understood to be a global problem in the 1930s.
Heavily furred marine mammals exposed to oil spills are affected in similar ways. Oil coats the fur of sea otters and seals, reducing its insulating effect, and leading to fluctuations in body temperature and hypothermia. Oil can also blind an animal, leaving it defenseless. The ingestion of oil causes dehydration and impairs the digestive process. Animals can be poisoned, and may die from oil entering the lungs or liver.
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. The chemicals from the oil which dissolve in water, and hence are available to bacteria, are those in the water associated fraction of the oil.
In addition, oil spills can also harm air quality. The chemicals in crude oil are mostly hydrocarbons that contains toxic chemicals such as benzenes, toluene, poly-aromatic hydrocarbon and oxygenated polycyclic aromatic hydrocarbons. These chemicals can introduce adverse health effects when being inhaled into human body. In addition, these chemicals can be oxidized by oxidants in the atmosphere to form fine particulate matter after they evaporate into the atmosphere. These particulates can penetrate lungs and carry toxic chemicals into the human body. Burning surface oil can also be a source for pollution such as soot particles. During the cleanup and recovery process, it will also generate air pollutants such as nitric oxides and ozone from ships. Lastly, bubble bursting can also be a generation pathway for particulate matter during an oil spill. During the Deepwater Horizon oil spill, significant air quality issues were found on the Gulf Coast, which is the downwind of DWH oil spill. Air quality monitoring data showed that criteria pollutants had exceeded the health-based standard in the coastal regions.
Sources and rate of occurrence
Oil spills can be caused by human error, natural disasters, technical failures or deliberate releases. It is estimated that 30-50% of all oil spills are directly or indirectly caused by human error, with approximately 20-40% of oil spills being attributed to equipment failure or malfunction. Causes of oil spills are further distinguished between deliberate releases, such as operational discharges or acts of war and accidental releases. Accidental oil spills are in the focus of the literature, although some of the largest oil spills ever recorded, the Gulf War Oil Spill (sea based) and Kuwaiti Oil Fires (land based) were deliberate acts of war. The academic study of sources and causes of oil spills identifies vulnerable points in oil transportation infrastructure and calculates the likelihood of oil spills happening. This can then guide prevention efforts and regulation policies
Around 40-50% of all oil released into the oceans stems from natural seeps from seafloor rocks. This corresponds to approximately 600,000 tons annually on a global level. While natural seeps are the single largest source of oil spills, they are considered less problematic because ecosystems have adapted to such regular releases. For instance, on sites of natural oil seeps, ocean bacteria have evolved to digest oil molecules.
Oil tankers and vessels
Vessels can be the source of oil spills either through operational releases of oil or in the case of oil tanker accidents. Operational discharges from vessels are estimated to account for 21% of oil releases from vessels. They occur as a consequence of failure to comply with regulations or arbitrary discharges of waste oil and water containing such oil residues. Such operational discharges are regulated through the MARPOL convention. Operational releases are frequent, but small in the amount of oil spilled per release, and are often not in the focus of attention regarding oil spills. There has been a steady decrease of operational discharges of oil, with an additional decrease of around 50% since the 1990s.
Accidental oil tank vessel spills account for approximately 8-13% of all oil spilled into the oceans. The main causes of oil tank vessel spills are collision (29%), grounding (22%), mishandling (14%) and sinking (12%), among others. Oil tanker spills are considered a major ecological threat due to the large amount of oil spilled per accident and the fact that major sea traffic routes are close to Large Marine Ecosystems. Around 90% of the world's oil transportation is through oil tankers, and the absolute amount of seaborne oil trade is steadily increasing. However, there has been a reduction of the number of spills from oil tankers and of the amount of oil released per oil tanker spill. In 1992, MARPOL was ammended and made it mandatory for large tankers (5,000 dwt and more) to be fitted with double hulls. This is considered to be a major reason for the reduction of oil tanker spills, alongside other innovations such as GPS, sectioning of vessels and sea lanes in narrow straits.
Offshore oil platforms
Accidental spills from oil platforms nowadays account for approximately 3% of oil spills in the oceans. Prominent offshore oil platform spills typically occurred as a result of a blowout. They can go on for months until relief wells have been drilled, resulting in enormous amounts of oil leaked. Notable examples of such oil spills are Deepwater Horizon and Ixtoc I. While technologies for drilling in deep water have significantly improved in the past 30-40 years, oil companies move to drilling sites in more and more difficult places. This ambiguous development results in no clear trend regarding the frequency of offshore oil platform spills.
Pipelines as sources of oil spills are estimated to contribute 1% of oil pollution to the oceans. Reasons for this are underreporting, and many oil pipeline leaks occur on land with only fractions of that oil reaching the oceans. Overall, however, there has been a substancial increase of pipeline oil spills in the past four decades. Prominent examples include oil spills of pipelines in the Niger Delta. Pipeline oil spills can be caused by trawling of fishing boats, natural disasters, pipe corrosion, construction defects and deliberate sabotage or attacks, as with the Caño Limón-Coveñas pipeline in Colombia.
Oil can reach the oceans as oil and fuel from land-based sources. It is estimated that runoff oil and oil from rivers are responsible for 11% of oil pollution to the oceans. Such pollution can also be oil on roads from land vehicles, which is then flushed into the oceans during rainstorms. Purely land-based oil spills are different from maritime oil spills in that oil on land does not spread as quickly as in water, and effects thus remain local.
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. Physical cleanups of oil spills are also very expensive. However, microorganisms such as Fusobacteria species demonstrate potential for future oil spill cleanup because of their ability to colonize and degrade oil slicks on the sea surface.
- Bioremediation: use of microorganisms or biological agents to break down or remove oil; such as Alcanivorax bacteria or Methylocella silvestris.
- Bioremediation Accelerator: a binder molecule that moves hydrocarbons out of water and into gels, when combined with nutrients, encourages natural bioremediation. Oleophilic, hydrophobic chemical, containing no bacteria, which chemically and physically bonds to both soluble and insoluble hydrocarbons. The accelerator acts as a herding agent in water and on the surface, floating molecules such as phenol and BTEX to the surface of the water, 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.
- 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 can be used to dissipate oil slicks. A dispersant is either a non-surface active polymer or a surface-active substance added to a suspension, usually a colloid, to improve the separation of particles and to prevent settling or clumping. They may rapidly disperse large amounts of certain oil types from the sea surface by transferring it into the water column. They will cause the oil slick to break up and form water-soluble micelles that are rapidly diluted. The oil is then effectively spread throughout a larger volume of water than the surface from where the oil was dispersed. They can also delay the formation of persistent oil-in-water emulsions. However, laboratory experiments showed that dispersants increased toxic hydrocarbon levels in fish by a factor of up to 100 and may kill fish eggs. Dispersed oil droplets infiltrate into deeper water and can lethally contaminate coral. Research indicates that some dispersants are toxic to corals. A 2012 study found that Corexit dispersant had increased the toxicity of oil by up to 52 times. In 2019, the U.S. National Academies released a report analyzing the advantages and disadvantages of several response methods and tools.
- 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.
- Dredging: for oils dispersed with detergents and other oils denser than water.
- Skimming: Requires calm waters at all times during the process. Vessels used for skimming clean up are called Gulp Oil Skimmers.
- Solidifying: Solidifiers are composed of tiny, floating, dry ice pellets, and hydrophobic polymers that both adsorb and absorb. They clean up oil spills by changing the physical state of spilled oil from liquid to a solid, 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 wildlife and have been proven to suppress harmful vapors commonly associated with hydrocarbons such as benzene, xylene and naphtha. The reaction time for solidification of oil is controlled by the surface area or size of the polymer or dry pellets as well as the viscosity and thickness of the oil layer. Some solidifier product manufacturers claim the solidified oil can be thawed and used if frozen with dry ice or 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 at Dauphin Island and Fort Morgan, Alabama, 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.
- Beach Raking: coagulated oil that is left on the beach can be picked up by machinery.
- 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 and adsorb small droplets
- Chemical and biological agents: helps to break down the oil
- Vacuums: remove oil from beaches and water surface
- Shovels and other road equipment: typically used to clean up oil on beaches
- Secondary containment – methods to prevent releases of oil or hydrocarbons into the environment.
- Oil Spill Prevention Control 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.
- Thick-hulled railroad transport tanks.
Spill response procedures should include elements such as;
- A listing of appropriate protective clothing, safety equipment, and cleanup materials required for spill cleanup (gloves, respirators, etc.) and an explanation of their proper use;
- Appropriate evacuation zones and procedures;
- Availability of fire suppression equipment;
- Disposal containers for spill cleanup materials; and
- The first aid procedures that might be required.
Environmental Sensitivity Index (ESI) mapping
Environmental Sensitivity Indexes (ESI) are tools used to create Environmental Sensitivity Maps (ESM). ESM’s are pre-planning tools used to identify sensitive areas and resources prior to an oil spill event in order to set priorities for protection and plan clean-up strategies. It is to date the most commonly used mapping tool for sensitive area plotting. The ESI has three components: A shoreline type ranking system, a biological resources section, and a human-use resource category.
History and Development
ESI is the most frequently used sensitivity mapping tool yet. It was first applied in 1979 in response to an oil-spill near Texas in the Gulf of Mexico. To this time, ESI maps were prepared merely days in advance of one’s arrival to an oil spill location. ESMs used to be atlases, maps consisting of thousands of pages that could solely work with spills in the oceans. In the past 3 decades, this product has been transformed into a versatile online tool. This conversion allows sensitivity indexing to become more adaptable and in 1995 by the US National Oceanic and Atmospheric Administration (NOAA) worked on the tool allowing ESI to extended maps to lakes, rivers, and estuary shoreline types. ESI maps have since become integral to collecting, synthesizing, and producing data which have previously never been accessible in digital formats. Especially in the United States, the tool has made impressive advancements in developing tidal bay protection strategies, collecting seasonal information and generally in the modelling of sensitive areas. Together with Geographic Information System Mapping (GIS), ESI integrates their techniques to successfully geographically reference the three different types of resources.
Usage and Application
The ESI depicts environmental stability, coastal resilience to maritime related catastrophes, and the configurations of a stress-response relationship between all things maritime. Created for ecological-related decision making, ESMs can accurately identify sensitive areas and habitats, clean-up responses, response measures and monitoring strategies for oil-spills. The maps allow experts from varying fields to come together and work efficiently during fast paced response operations. The process of making an ESI atlas involves GIS technology. The steps involve, first zoning the area that is to be mapped, and secondly, a meeting with local and regional experts on the area and its resources. Following, all the shoreline types, biological, and human use resources need to be identified and their locations pinpointed. Once all this information is gathered, it then becomes digitized. In its digital format, classifications are set in place, tables are produced and local experts refine the product before it gets released.
ESI’s current most common use is within contingency planning. After the maps are calculated and produced, the most sensitive areas get picked out and authenticated. These areas then go through a scrutinization process throughout which methods of protection and resource assessments are obtained. This in-depth research is then put back into the ESMs to develop their accuracy and allowing for tactical information to be stored in them as well. The finished maps are then used for drills and trainings for clean-up efficiency. Trainings also often help to update the maps and tweak certain flaws that might have occurred in the previous steps.
Shoreline type is classified by rank depending on how easy the target site would be to clean up, how long the oil would persist, and how sensitive the shoreline is. The ranking system works on a 10-point scale where the higher the rank, the more sensitive a habitat or shore is. The coding system usually works in colour, where warm colours are used for the increasingly sensitive types and cooler colours are used for robust shores. For each navigable body of water, there is a feature classifying its sensitivity to oil. Shoreline type mapping codes a large range of ecological settings including estuarine, lacustrine, and riverine environments. 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. Hence ESI shoreline ranking helps committees identify which clean-up techniques are approved or detrimental the natural environment. 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. Mangroves and marshes tend to have higher ESI rankings due to the potentially long-lasting and damaging effects of both 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.
Within the biological resources, the ESI maps protected areas as well as those with bio-diverse importance. These are usually identified through the UNEP-WCMC Integrated Biodiversity Assessment Tool. There are varying types of coastal habitats and ecosystems and thus also many endangered species that need to be considered when looking at affected areas post oil spills. The 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. Necessary when ranking and selecting species is their vulnerability to the oil spills themselves. This not only includes their reactions to such events but also their fragility, the scale of large clusters of animals, whether special life stages occur ashore, and whether any present species is threatened, endangered or rare. The way in which the biological resources are mapped is through symbols representing the species, and polygons and lines to map out the special extent of the species. The symbols also have the ability to identify the most vulnerable of a species life stages, such as the molting, nesting, hatching or migration patterns. This allows for more accurate response plans during those given periods. There is also a division for sub-tidal habitats which are equally important to coastal biodiversity including kelp, coral reefs and sea beds which are not commonly mapped within the shoreline ESI type.
Human-use resources are also often referred to as socio-economic features, which map inanimate resources that have the potential to be directly impacted by oil pollution. Human-use resources that are mapped within the ESI will have socio-economic repercussions to an oil spill. These 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, and resource origins. Some examples include airports, diving sites, popular beach sites, marinas, hotels, factories, natural reserves or marine sanctuaries. When mapped, the human-use resources the need protecting must be certified by a local or regional policy maker. These resources are often extremely vulnerable to seasonal changes due to ex. fishing and tourism. For this category there are also a set of symbols available to demonstrate their importance on ESMs.
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.
|Film thickness||Quantity spread|
|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. 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.
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