Oil spill
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An oil spill is the release of a liquid
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.[1] Spills may take weeks, months or even years to clean up.[2]
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.[3]
Human impacts
An oil spill represents an immediate negative effects on human health, including respiratory and reproductive problems as well as liver, and immune system damage. Oil spills causing future oil supply to decline also effects the everyday life of humans such as the potential closure of beaches, parks, fisheries and fire hazards. The
Spilled oil can also contaminate drinking water supplies. For example, in 2013 two different oil spills contaminated water supplies for 300,000 in
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.
Environmental effects
Animals
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.[9] 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.[10]
In general, spilled oil can affect animals and plants in two ways: dirесt from the oil and from the response or cleanup process.[11][12][13][14] 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 do so 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
Heavily furred
Air
In addition, oil spills can also harm air quality.
Ecosystems, habitat
The majority of oil from an oil spill remains in the environment, hence a spill from an operation in the ocean is different from an operation on tundra or wetland. Wetlands are considered one of the most sensitive habitats to oil spills and the most difficult to clean.[28]
Sources and rate of occurrence
Oil spills can be caused by human error, natural disasters, technical failures or deliberate releases.
Natural seeps
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.[34][35][32]
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. As of 2007, operational discharges from vessels were estimated to account for 21% of oil releases from vessels.[35] They occur as a consequence of failure to comply with regulations or arbitrary discharges of waste oil and water containing such oil residues.[36] Such operational discharges are regulated through the MARPOL convention.[37] 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.[35] There has been a steady decrease of operational discharges of oil, with an additional decrease of around 50% since the 1990s.[32]
As of 2007,[update] accidental oil tank vessel spills accounted for approximately 8–13% of all oil spilled into the oceans.
In 2023, the International Tanker Owners Pollution Federation (ITOPF) documented a significant oil spill incident of over 700 tonnes and nine medium spills ranging between 7 to 700 tonnes. The major spill occurred in Asia involving heavy fuel oil, and the medium spills were scattered across Asia, Africa, Europe, and America, involving various oil types.[41]
The total volume of oil released from these spills in 2023 was approximately 2,000 tonnes. This contributes to a trend of decreased oil spill volumes and frequencies over the decades. Comparatively, the 1970s averaged 79 significant spills per year, which drastically reduced to an average of about 6.3 per year in the 2010s, and has maintained a similar level in the current decade.[41]
The reduction in oil spill volume has also been substantial over the years. For instance, the 1990s recorded 1,134,000 tonnes lost, mainly from 10 major spills. This figure decreased to 196,000 tonnes in the 2000s and 164,000 tonnes in the 2010s. In the early 2020s, approximately 28,000 tonnes have been lost, predominantly from major incidents.[41]
Offshore oil platforms
Accidental spills from oil platforms nowadays account for approximately 3% of oil spills in the oceans.[35] 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.[32] 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.[32]
Pipelines
As of 2010, overall, there has been a substantial increase of pipeline oil spills in the past four decades.[32] 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, sabotage, or an attack,[36] as with the Caño Limón-Coveñas pipeline in Colombia.
Other sources
Oil can reach the oceans as oil and fuel from land-based sources.[31] It is estimated that runoff oil and oil from rivers are responsible for 11% of oil pollution to the oceans.[35] Such pollution can also be oil on roads from land vehicles, which is then flushed into the oceans during rainstorms.[34] 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.[31]
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.[1] Physical cleanups of oil spills are also very expensive. Until the 1960s, the best method for remediation consisted of putting straw on the spill and retrieving the oil-soaked straw manually.[42] Chemical remediation is the norm as of the early 21st Century, using compounds that can herd and thicken oil for physical recovery, disperse oil in the water, or facilitate burning the oil off.[42] The future of oil cleanup technology is likely the use of microorganisms such as Fusobacteriota (formerly Fusobacteria), species demonstrate potential for future oil spill cleanup because of their ability to colonize and degrade oil slicks on the sea surface.[42][43]
There are three kinds of oil-consuming bacteria.
Methods for cleaning up include:[44]
- biological agents[46] to break down or remove oil; such as Alcanivorax bacteria[47] or Methylocella silvestris.[48]
- 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.[49]
- Controlled burning can effectively reduce the amount of oil in water, if done properly.[50] But it can only be done in low wind,[51] and can cause air pollution.[52]
- 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.[54] Dispersed oil droplets infiltrate into deeper water and can lethally contaminate coral. Research indicates that some dispersants are toxic to corals.[55] A 2012 study found that Corexit dispersant had increased the toxicity of oil by up to 52 times.[56] In 2019, the U.S. National Academies released a report analyzing the advantages and disadvantages of several response methods and tools.[57]
- 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.[58]
- Dredging: for oils dispersed with detergents and other oils denser than water.
- Skimming: Requires calm waters at all times during the process.
- Solidifying: Solidifiers are composed of tiny, floating, 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 spillcleanup.
- 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.[62]
- Beach Raking: coagulated oil that is left on the beach can be picked up by machinery.
Equipment used includes:[50]
- 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 [63]
- 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
Prevention
- 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.[64]
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.[65]
Research
- Adaptation of the oil bee's, e.g. Macropis fulvipes', mechanism for harvesting flower oils has led to the biomimetic development of an additional oil spill recovery method. Oil bees have oleophilic properties in their hair-like protrusions that collect and store oil. This technique has been applied to textiles that can be used to remove oil from sea water.[66]
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.[67][68] It is to date the most commonly used mapping tool for sensitive area plotting.[69] The ESI has three components: A shoreline type ranking system, a biological resources section, and a human-use resource category.[70]
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.[69] 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.[70] 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.[69] Together with Geographic Information System Mapping (GIS), ESI integrates their techniques to successfully geographically reference the three different types of resources.[71]
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.[72] 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.[73] 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.[74] 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.[74] 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.[74] Trainings also often help to update the maps and tweak certain flaws that might have occurred in the previous steps.
ESI Categories
Shoreline type
Biological resources
Within the biological resources, the ESI maps protected areas as well as those with bio-diverse importance. These are usually identified through the
Human-use resources
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:
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.[79]
Film thickness | Quantity spread | ||||
---|---|---|---|---|---|
Appearance | inches | 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.
Largest oil spills
Crude oil and refined fuel spills from tanker ship accidents have damaged vulnerable
Oil spills in the Niger Delta are among the worst on the planet and is often used as an example of ecocide.[84][85][86][87][88] Between 1970 and 2000, there were over 7,000 spills. Between 1956 and 2006, up to 1.5 million tons of oil were spilled in the Niger Delta.[88]
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
Spill / Tanker | Location | Date | Tonnes of crude oil (thousands)[a] |
Barrels (thousands) |
US Gallons (thousands) |
References |
---|---|---|---|---|---|---|
Kuwaiti Oil Fires[b]
|
Kuwait | January 16, 1991 – November 6, 1991 | 136,000 | 1,000,000 | 42,000,000 | [89][90] |
Kuwaiti Oil Lakes [c] | Kuwait | January 1991 – November 1991 | 3,409–6,818 | 25,000–50,000 | 1,050,000–2,100,000 | [91][92][93] |
Lakeview Gusher | Kern County, California, USA | March 14, 1910 – September 1911 | 1,200 | 9,000 | 378,000 | [94] |
Gulf War oil spill [d] | Kuwait, Iraq, and the Persian Gulf | January 19, 1991 – January 28, 1991 | 818–1,091 | 6,000–8,000 | 252,000–336,000 | [92][96][97] |
Deepwater Horizon | United States, Gulf of Mexico | April 20, 2010 – July 15, 2010 | 560–585 | 4,100–4,900 | 189,000–231,000 | [98][99][100][101][102] |
Ixtoc I | Mexico, Gulf of Mexico | June 3, 1979 – March 23, 1980 | 454–480 | 3,329–3,520 | 139,818–147,840 | [103][104][105] |
Atlantic Empress / Aegean Captain
|
Trinidad and Tobago | July 19, 1979 | 287 | 2,105 | 88,396 | [106][107][108] |
Fergana Valley
|
Uzbekistan | March 2, 1992 | 285 | 2,090 | 87,780 | [109] |
Nowruz Field Platform
|
Iran, Persian Gulf | February 4, 1983 | 260 | 1,900 | 80,000 | [110] |
ABT Summer | Angola, 700 nmi (1,300 km; 810 mi) offshore | May 28, 1991 | 260 | 1,907 | 80,080 | [106] |
Castillo de Bellver
|
South Africa, Saldanha Bay | August 6, 1983 | 252 | 1,848 | 77,616 | [106] |
Amoco Cadiz | France, Brittany | March 16, 1978 | 223 | 1,635 | 68,684 | [106][109][111][112] |
Taylor Energy
|
United States, Gulf of Mexico | September 23, 2004 – Present | 210–490 | 1,500–3,500 | 63,000–147,000 | [113] |
Odyssey | off the coast of Nova Scotia, Canada | November 10, 1988 | 132 | 968 | 40,704 | [114] |
Torrey Canyon | England, Cornwall | March 18, 1967 | 119 | 872 | 36,635 | [115] |
- ^ 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.[91]
- ^ 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.[95] 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).
The economic impact of oil spills
Oil spills can have devastating environmental impacts; however, we cannot allow these to overshadow their often equally detrimental economic consequences.[116] These disasters do not only pose immediate threats to marine ecosystems, but also leave lasting impacts on local and regional economies. This section will explore the multifaceted economic repercussions of oil spills, specifically considering: the decline in tourism, the reduction in fishing, and the impact on port activity.
Decline in tourism
In the short term, an oil spill will prevent tourists from partaking in usual recreational activities such as swimming, boating, diving, and angling.[117] As such, the area will witness a decline in tourism. This will negatively impact several industries. Firstly, the hotels, restaurants, and bars in the immediate vicinity will have significantly fewer customers. Local car park owners and shopkeepers will be affected too. Then, this decline in tourists will cause further damage to travel agencies, tour guides, and transport companies.[118] The beaches will likely stay shut for several days whilst clean-up operations take place, and there may be disruption caused by an increase in clean-up vehicles.[117] Overall, several businesses will be negatively impacted by the spill in the short term, which can lead to further long-term damage should companies be forced to reduce staff or shut down entirely.
Often, this process is intensified by disproportionate media attention. Usually, the affected area returns to normal relatively soon after an oil spill, as the clean-up process is fast.[117] However, media stories will drive future tourists away, as they work to degrade the popular image of a destination with exaggerated stories of oil on beaches and deserted hotels.[117] This aggravates the economic losses, as people continue to choose to travel elsewhere. Such a scenario is particularly damaging for regions which are very reliant on the tourism industry.[119] For example, the Brazilian Northeast can be very vulnerable to drops in tourism, thus, they were badly impacted following a 2500 tonne crude oil spill from an unknown tanker in 2019.[120]
Similarly, tourism in Ibiza was severely impacted in 2007. Just 20 tonnes of oil were spilled from the Don Pedro in July 2007, a relatively limited volume compared with other spills. Whilst this caused just a small amount of environmental damage, the economic damage was disproportionately large. Most beaches were reopened within a week, just a dozen seabirds were affected, and there were no reports of injured sea mammals. Nonetheless, 27 percent of hotels in Ibiza were negatively affected, with two thirds of these being seafront hotels. Thus, 32 claims were made by tourist firms, equating to approximately 1.5 million euros of compensation.[121] This provides a clear example of an oil spill resulting in massive economic disaster. Furthermore, following the world’s largest oil spill, the Deepwater Horizon Oil Spill in 2010,[122] the U.S. Travel Association estimated 23 billion dollars’ worth of associated costs for affected tourist infrastructure.[123]
Reduction in fishing
After the Deepwater Horizon crisis,[124] the Gulf of Mexico suffered an estimated 1.9-billion-dollar loss in revenue from fishing. This is because fishing closures were imposed due to fears of the safety of seafood,[125] there was also a decline in demand, as seafood restaurants and markets suffered such severe losses that many were forced to shut.[117] Usually, the Gulf sees an average of 106,703 fishing trips per day,[126] equating to 1 million metric tonnes of annual fishery landings.[127] Therefore, the necessary fishing ban following the disaster was highly damaging. Similarly, following the sinking of the Prestige oil tanker near Galicia, Spain, in November 2002, 77,000 tonnes of crude oil were spilled into the ocean. This disaster has had severe economic consequences, alongside the environmental damage. Large zones were cordoned in which fishing was banned, with these bans lasting for more than eight months. This affected several groups, including fishermen, ship owners, and the companies who bought and sold the fish. Several compensatory actions were introduced, including tax benefits and aid. This resulted in expenses of approximately 113 million euros in an attempt to compensate for the halt in fishing activity.[128] The examples of the Deepwater Horizon and the Prestige clearly illustrate the severe economic consequences when oil spills prevent commercial fishing.
Water pollution due to oil spills can be severe, often resulting in the death or injury of many sea creatures, including birds, sea mammals, fish, algae, and coral.[129] The impact on fish caught in the spill has both immediate and longer-term impacts. Immediately, the fish are tainted with oil, and they cannot be used commercially due to safety reasons. Then, the oil can spread and sink below the water’s surface. If fish swallow the oil, they are also inconsumable due to the health risk posed to humans.[130] Therefore, massive economic damage is caused to the fishing industry following an oil spill, as the stock is vastly reduced. Furthermore, the oil can cause damage to the equipment and boats of fishermen. Clean-up operations can also interrupt usual fishing routes, and sometimes fishing bans are imposed.[131] This further illustrates the damaging economic effects of oil spills on commercial fishing, which is particularly detrimental for regions whose economy relies heavily on fishing.
The impact on port activity
Ports are major hubs for economic activity; thus, an oil spill in or near a port can have significant consequences.[132] During and following a spill, all boats entering or leaving the port must be closely managed in order to prevent further spread. Furthermore, specialist cleaning contractors must be hired to effectively clean the various port structures.[117] Oil spills are relatively regular occurrences in ports, as small spills often happen due to the large volume of boats, and these are not as well documented in the media as larger events are.[133] However, these spills must still be dealt with, and they can still have damaging economic repercussions.[134] Both the incident and the response require expensive and time-consuming management which is disruptive to port activity.[135] Furthermore, special care must be taken during clean-up operations to ensure that the oil does not get stuck under the quayside, as this could act as a continual source of oil contamination.[136] This can also be seen with sea defenses; should the oil penetrate deep into the structures, they may become a source of secondary pollution.[117] Therefore, it is crucial for ports to manage and mitigate any oil spills, in order to limit the damage to ships and shipping operations. Otherwise, should large disruption occur, the economic damage can be extensive due to costly clean-up processes and delayed shipments.
Summary
The economic impact of oil spills on tourism, fishing, and ports is substantial and important to assess. Coordinated efforts are necessary to mitigate these impacts, including effective clean-up measures, public relations campaigns to restore the image of affected areas, and support for businesses and communities that must bear the economic downturn.
See also
- Automated Data Inquiry for Oil Spills
- Environmental issues with petroleum
- Environmental issues with shipping
- LNG spill
- Storm oil
- 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)
- ShoreZone
- Spill containment
- Tarball
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{{cite news}}
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Further reading
- Nelson-Smith, Oil Pollution and Marine Ecology, Elek Scientific, London, 1972; Plenum, New York, 1973
- Oil Spill Case Histories 1967–1991, NOAA/Hazardous Materials and Response Division, Seattle, WA, 1992
- Ramseur, Jonathan L. Oil Spills: Background and Governance, Congressional Research Service, Washington, DC, September 15, 2017