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Oil is a general term used
to denote petroleum products, which mainly consist of hydrocarbons.
Crude oils are made up of a wide spectrum of hydrocarbons ranging
from very volatile, light materials such as propane and benzene
to more complex heavy compounds such as bitumens, asphaltenes, resins
and waxes. Refined products such as petrol or fuel oil are composed
of smaller and more specific ranges of these hydrocarbons.
With petroleum finding a wide
range of applications in the form of vehicle fuel, heating source
for homes and industry, for electricity generation and in basic
industrial operations, there has been an enormous demand for production
and movement of oil. Oil is thus being continuously pumped from
the ground, refined, transported and stored, resulting in spilling
by “operations” or “accidents”.

Oil Spills have been a major
cause of concern as they pose a danger to public health, devastate
natural resources and disrupt the economy. When we think of oil
spills, we usually think of oil tankers spilling their cargo in
the seas and oceans. But the spills can be due to any operations
and accidents occurring in the oil industry. As shown in the Table
below, the spills can result due to various operations taking place
during the generation or movement of oil:
OPERATIONS |
< 7
tons |
7 - 700
tons |
> 700
tons |
Total |
Loading/ Discharging |
2767 |
299 |
17 |
3083 |
Bunkering |
541 |
25 |
0 |
566 |
Other Operations |
1167 |
47 |
0 |
1214 |
ACCIDENTS |
|
|
|
|
Collisions |
163 |
254 |
87 |
504 |
Groundings |
222 |
200 |
106 |
528 |
Hull failures |
562 |
77 |
43 |
682 |
Fires & explosions |
150 |
16 |
19 |
185 |
Other/ Unknown |
2221 |
165 |
37 |
2423 |
TOTAL |
7793 |
1083 |
309 |
9185 |
Table 1. Incidence of Spill by
Cause
From this table, it can be deduced
clearly that main spills are caused during the loading and discharging
operations although accidents play a considerable part in oil pollution
caused by oil spills.

Picture
1: IXTOC I exploratory well blew out on June 3,1997 in the Bay of
Campeche of Cuidad del Carmen, Mexico. The accident resulted in
spilling of 140 million gallons of oil.

Picture 2: Part of an oil
slick of some 20 miles, follows the stricken Bahamas-flagged, ‘Prestige’ oil tanker, as it is towed away from the
northwestern coast of Spain near Maxi by two tugboats to avoid
an environmental catastrophe, Tuesday Nov 14,2002.
The history of incidents related
to oil spills due to Tankers gives us an idea of the great danger
posed to the oceanic environment due to oil spills. Some of the
major accidents related to the oil industry have been due to tankers
and are listed below:
Year |
Name |
Place |
Tons |
1978 |
Amoco Cadiz |
Brittany |
222,000 |
1979 |
Atlantic Empress |
Tobago |
160,000 |
1967 |
Torrey Canyon |
UK |
119,000 |
1993 |
Braer |
Shetland Isles |
85,000 |
1996 |
Sea Empress |
Milford Haven |
72,000 |
1989 |
Exxon Valdez |
Alaska |
38,800 |
Table 2: Six Major Tanker Spills
The Table above can give us
a clear perspective of the amount of crude oil entering our oceans
over the time, resulting in a tremendous loss of aquatic wildlife
and endangering the human population around the accident site, for
years after the incident

Picture 3: The oil spill
in the Manawa River.

Picture 4: About 38.3 million
litters of crude oil gushed out of a storage tank at Brachia,
Las Minas, Panama

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Equipment breaking down:
- During these processes of generating and moving oil, spills
can occur due to accidents involving tankers, barges, pipelines,
refineries and storage facilities

Picture 5: In December 1992,
Aegean Sea tanker ran aground off the port of La Coruna in north-west
Spain, broke up and finally exploded, emptying its entire cargo
of about 79,000 tons of crude oil into the sea.
- Natural reasons:
- Spills can also be caused by natural disasters like hurricanes.
Oil has been in the environment for a long time. Some oil lies below
the ocean floor and can seep into the ocean through cracks.
- Man-made reasons:
- Sometimes when people change the oil in their cars, they dump
the used, dirty oil on the ground and as an action of rain; this
oil is carried down to the streams. The amount of oil dumped on
the ground for a year can easily surpass a serious oil tanker spill.
Deliberate acts by countries at war can also be a major cause for
oil spills.

Predominantly, an oil spill
is related to the spills caused due to accidents involving tankers,
causing a serious impact on coastal activities and on those who
exploit the resources of the sea. The severity of impact of an
oil spill depends on a lot of factors, including the characteristics
of oil and natural conditions prevalent at the time of the spill.
The
effects of oil spills can be divided broadly into following specifications-
- Marine contamination
- Marine life can be affected by both the
physical and chemical properties of
the oil spilled, the main threat posed by the residues on the
contaminated sea surface. A short-term exposure can render unpleasant
tastes and smells to aquatic life but a prolonged exposure,
to even small concentrations of toxic components can impair
the ability of marine organisms to reproduce, grow, feed or
perform other functions. Another impact of oil spills can be
seen on the shorelines, where large areas of rocks, sand and
mud are affected, resulting in a loss of aesthetic value of
the beaches.

Picture
6: Oiled bird in Exxon Valdez Spill.
Picture7: 1989 Exxon Valdez
oil spill. Nearly one quarter of the rehabilitated and released
sea otters died soon after the release.

Picture
8: Between 300-400 spills per year occur in Alaska. Tens of thousands
of animals died in Exxon Valdez spill, 1989.

Picture
9: A bird floats in oil contaminated water in Camelle, northwestern
Spain, Sunday, Nov.17, 2002 after oil spilled from the Bahamas-flagged
tanker ‘Prestige’ washed ashore, Saturday.

Picture
10: A tanker laden 70,000 tons of fuel oil split in two off northwest
Spain November 19,2002.
Rescue workers shovel sand on the oil-covered beach in the fishery
village of Malpica, northern Spain.
- Fresh water contamination
- In fresh waters, oil contamination can
result in severe impacts on the
habitat because the movement associated with water is minimal,
as compared to marine environment. Stagnant water bodies cause
the oil to remain in the environment for long, resulting in
prolonged exposure of the plants and animals. Incase of flowing
streams and rivers, the oil not only tends to collect on plants
and grasses growing on the banks but also interacts with sediments,
thereby affecting the organisms.
-

Oil spills, whether or not
they are petroleum-based, pose an immediate threat to the environment
and require quick and thorough responses. It is important to prevent
the oil from spreading and causing further disruption to the subtle
ecosystem. The spills can lead to severe surface and groundwater
pollution, requiring efficient methods for the cleanup.
Oil spills cleanup techniques depend largely on the type of oil,
the conditions present at the location and during the time of
the spill. The various remediation processes can thus be broadly
divided into two categories:
a. Short Term Processes
b. Long Term Processes
Both these categories are the result of the
kind of techniques used for treatment of oils spills and the various
advantages and disadvantages of these techniques.

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Containment and Recovery
using Booms and Skimmers
This is usually the first measure
used to attempt to clean up after an oil spill. Long, floating plastic
or rubber barriers called booms are placed around the floating oil
slick. These acts like fences, containing the oil and preventing
it from further spreading. . In addition, booms may be used to divert
and channel oil slicks along desired paths, making them easier to
remove from the surface of the water. Booms can be divided into
several basic types. Fence booms have a high freeboard and a flat
flotation device, making them least effective in rough water, where
wave and wind action can cause the boom to twist. Round or curtain
booms have a more circular flotation device and a continuous skirt.
They perform well in rough water, but are more difficult to clean
and store than fence booms. Non-rigid or inflatable booms come in
many shapes. They are easy to clean and store, and they perform
well in rough seas. However, they tend to be expensive, more complicated
to use, and puncture and deflate easily. All boom types are greatly
affected by the conditions on the water; the higher the waves swell,
the less effective booms become.
Picture
11: Booms used to contain oil in the calm ocean waters.
Picture 12:
Containment booms used in the oceans to prevent further spreading
of the spill
After the oil is contained using booms, ‘skimmers’
or boats that skim spilled oil from the water surface are used.
In calm waters, vacuum skimmers work well to suck the oil and
put it into storage tanks. In choppy waters, floating disk and
rope skimmers can be passed through the oil.
Usually, booms and skimmers are the first technique employed to
remove oil from marine environments but this technique can recover
a very small proportion of the spilled oil. The only disadvantage
associated with this technique is that it hampers the natural
tendency of oil to spread and disperse. So, even though we deploy
this technique, after some time, the oil starts floating at a
very low rate rendering the technique ineffective.
- Absorption
Absorption is the technique employed in choppy
or fast moving waters, when methods like containment and removal
fail. In this method, sorbent materials such as talc, straw, sawdust
and synthetic absorbents are added to the oil slick and them removed
when they have soaked up some of the oil. These sorbent materials
act like a big sponge, removing oil but contaminated absorbent materials
must be treated as toxic waste and present disposal problems. Also,
straw and sawdust can become waterlogged and difficult to remove.

Picture
13: MYCELX oil spill absorbents are a breakthrough in shoreline
protection and absorb oil without absorbing water. Removes all hydrocarbons
and saves time, labor and disposal cost.
- Dispersants
Dispersant is a major remediation
method after oil spills.
a. How dispersant work?
Dispersants are chemicals that
promote the formation of tiny oil droplets, and delay the reformation
of slicks. They contain surfactants and/or solvent compounds.
Picture 14: Function of Surfactants
After an oil spill, oil droplets
break down because of waves and currents during the dispersion process.
Water and oil droplets then combined to a water-in-oil emulsion,
which has high viscosity. The balance between natural dispersion
and emulsification is set up.
Dispersants can alter this kind
of natural balance, inhibit emulsion formation and promote oil dispersion.
Thus they can remove the spilled oil from the water surface and
reduce the impact to environment, especially to the shoreline and
sensitive habitats.

b. The effectiveness of
dispersants depends on several factors.
1) Oil properties: Dispersant have little effect on very viscous,
floating oils. When oil weathers, its properties change. With the
passage of time, oil slicks become less and less dispersible.
2) Environmental conditions: For example, Water temperature. In
general, low temperatures will make oils more viscous and have some
minor effects on dispersant effectiveness. Dispersants work best
in warm water. Dispersants are sensitive to low salinity.
3) Spraying or aircraft/ship operations. Dispersants are applied
by spraying equipment mounted on boats of various sizes, small fixed
wing aircraft and helicopters. For large incidents, bigger fixed
wing aircraft can be used.

Picture 16b: Spraying by small fixed wing aircraft
Picture 16a: Spraying by Helicopter
Picture 15: Mechanism of Dispersants Remediation

Picture 16c: Spraying by Ship
c. Advantage of dispersant
1) Dispersants can rapidly treat
large area of spilled oil, especially through application of dispersant
from aircraft. This method can also handle spills occur in remote
areas. They are their key advantages over other methods. The benefit
of the appropriate use of dispersants was clearly demonstrated during
the response to the 'SEA EMPRESS' incident in 1996. In this case,
chemical dispersants prevented at least 17,000 tonnes of crude oil
from hitting the environmentally sensitive coastline of southwest
Wales.
2) Dispersants can be more effective
as compared to other techniques in extremely harsh weather conditions,
i.e. strong winds or currents.

Picture 17: Some 120 tons of dispersant was used to treat slicks in severe weather on the Shetland Isles, Scotland, 1993.
3) Dispersants assist the biodegradation
of the oil by increasing exposure to bacteria and oxygen. And the
biological processes further break the oil droplets to accelerate
the dispersion and dilution.
4) Dispersed oil droplets can
associate with suspended sediment, reducing risk of contamination
of marine habitats and wildlife.
d. Limitations of dispersants
1) Dispersants and/or dispersed
oil are toxic and may have long-term fate and effects on environment.
Dispersants promote the biodegradation process and make the oil
more available to organisms and enter the marine food chain. It
will cause lethal or harmful effects on planktonic plants, animals,
and fishes.
2) Dispersants may not be as
effective as other response techniques since they are affected greatly
by environmental condition. In the famous Exxon Valdez oil spill
in 1989, a trial dispersant was conducted, but was discontinued
eventually, because there was not enough wave action to mix the
dispersant with the oil in the water.
3) Dispersant spraying was ineffective on some crude oil and all
heavy fuel oil spilled because of their high viscosity.
e. Types of dispersants
1) ‘Type 1 dispersants’---Low
toxicity dispersants. This kind of dispersants is based on hydrocarbon
solvents with between 15 and 25% surfactant. They are of relatively
low effectiveness and need to be used at very high treatment rates.
2) ‘Type 2 dispersants’---More
efficient dispersants using a higher surfactant content. The higher
viscosity of these dispersants made them difficult to apply using
certain existing spraying mechanisms, but this was later overcome
by substituting some of the solvent with seawater.
3) ‘Type 3 dispersants’---
Higher performance dispersants using blends of different surfactant
types. Most modern dispersants can be sprayed from aircraft, and
from boats and ships.
f. Prospect of future dispersants:
Scientists are devoted into develop more advanced dispersants. The
goal is to improve the effectiveness of dispersants for heavy and
weathered oil and to develop dispersants with less toxic and long-term
cumulative effects are the main emphasis of future development.
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In-situ burning
In-situ burning of oil is
defined as the controlled burning of an oil spill on the water’s
surface. Burning requires minimal equipment although some specialized
equipment and training is required. Because the oil is gasified
during combustion, the need for physical collection, storage and
transport of recovered product is reduced but can cause air pollution
to a great extent. At times, burning also leaves a toxic residue
on the surface of water, causing more pollution rather than removing
it from the natural environment.

Picture 18: In-situ burning of oil when the oil still floating on the surface.

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Bioremediation
In-situ bioremediation is
becoming the preferred method for treating soil and ground water
affected by oil pollution. It is a process that uses microorganisms
to transform harmful organic compounds, like oil, into nontoxic
and less dangerous compounds. Even seawater contains a range of
microbes that can partially or completely degrade oil to water-soluble
compounds and eventually to carbon dioxide and water. Microorganisms
require nutrients (nitrogen and phosphorus) and organic carbon to
fuel continued growth and respiration. The water temperature and
the level of oxygen present also affect the efficiency of biodegradation.
The most favorable aspect of in-situ bioremediation, aside from
affordability, is that the cleanup can take place directly on the
site where there is pollution.
As bioremediation requires oxygen, this process can only take place
at the oil-water interface. Other factors that may slow bioremediation
are concentrations of contaminants being so high they are toxic
to microbes, unfavorable moisture and temperature. Altering environmental
conditions, adding nutrients or additional microbes and stimulating
microorganisms with electric charges can increase microbe activity
and bioremediation.
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