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DEPARTMENT OF MARINE TECHNOLOGY
FACULTY OF MECHANICAL ENGINEERING
UNIVERSITI TEKNOLOGI MALAYSIA

OIL FATE AND SLICK TRAJECTORY PREDICTIONS
FOR MARINE OIL POLLUTION CONTROL
STRATEGIES
(MMK1180)
NAME :
MATRIC No. :

MOHAMMED ALI AL-MUHANDES
MM091250

SUPERVISORS :
BIN AHMAD

MAIN : ASSOC. PROF. DR. ZAMANI
CO. : DR. JASWAR
1. INTRODUCTION

1.1 RESEARCH BACKGROUND
O’conneli (2006) stated that oil pollution affects on :


Fisheries and aquaculture resources ,



Tourism and,



Costal industries

In this research:


It is essential to predict the oil fate and slick trajectory



Combating strategies need to be set



Through simulation
1.2 PROBLEM STATEMENT

Oil pollution control strategies need to be
developed for each oil fate and slick trajectory
scenario. Since each scenario is unique and
independent, simulation method is preferred.
1.3 OBJECTIVE

To develop a method of choosing oil pollution combating
strategies
2. LITERATURE REVIEW
i.

Oil fate; The most important processes are spreading, evaporation, dispersion
viscosity and emulsification (O’connel, 2006c).

ii.

Slick trajectory; When an oil slick is predicted to affect on high sensitive
area, this prediction helps the decision maker significantly to choose the

combating strategies.
iii.

Types of shorelines; according to geographical shape, types of beaches

and to the environmental and socio-economic activities (IPIECA 2008a).
iv.

In-hand equipment and combating strategies; the limitation of spill control
techniques must be taken into consideration in determining the most appropriate
clean up response (Persga, 2009a). All of on-scene commanders are allowed to
take whatever action is appropriate to clean up and/or mitigate the effects of an

oil spill (Ch'ng,1997).
CONT.

72 references have been used in the thesis
3. RESEARCH METHODOLOGY
Determine oil fate
and slick trajectory
criteria


Determine oil fate and
slick trajectory

Determine protection
priority and types of
shorelines
Determine
equipment and
techniques
Determine
strategy
Validation by
Case of study
3.1 DETERMINATION OF OIL FATE

Item
Spreading
Evaporation
Dispersion
Viscosity
Emulsification

Using method
Lehr’s relationships (math. equation) for
major and minor diameters of ellipse
ADIOS2 (software)
ADIOS2 (software)
ADIOS2 (software)
Mackay’s relationship (math. equation)
3.2 DETERMINATION OIL SLICK TRAJECTORY

The oil slick trajectory was calculated using slick
trajectory calculator software based on:


Wind effects 3% of its speed in its direction
within specific time



Current affects 100% of its speed in its direction
within the same specific time
3.3 PROTECTION PRIORITY AND TYPES OF SHORELINES





Biological resources
high priority
Mangrove
Human use features
high priority
Water intake and port
Shorelines
high priority
Mangrove
3.4 EQUIPMENT AND USED TECHNIQUES
Techniques

Equipment

Containment and protection booming

Booms : Fence; Air inflated; Shoreline
. .
sealing

Recovery

Skimmers: Weir; Oleophilic; Vacuum;
.
Mechanical
Pumps: Archimedean; Reciprocating;
.
Peristaltic; Diaphragm;
Centrifugal

Dispersion

spray system mounted on
workboat
Airplane
Helicopter

Clean up

Sorbents: Inorganic, Natural organic and
Synthetic
Motorized equipment
Manual equipment
3.5 DETERMINE STRATEGY

Offshore recovery strategy

i.



ii.
iii.
iv.

Skimmers
pumps

Offshore dispersion strategy
Shoreline clean up and recovery strategy
Shoreline protection strategy
COMBATING STRATEGY FLOW CHART
CONT.
CONT.
3.5.1 OFFSHORE RECOVERY STRATEGY
3.5.1.1 SKIMMERS
3.5.1.2 PUMPS
3.5.2 OFFSHORE DISPERSION

The applying dispersant according to equations covered the following:
Application rate Vdis (litre/hectare)
Application rate Qdis (litre/sec)
Required speed (knot)
3.5.3 SHORELINE CLEAN UP AND RECOVERY STRATEGY
3.5.4 SHORELINE PROTECTION STRATEGY
3.6 CASE OF STUDY
The oil spill incident is simulated at area extended from 10 09’ N to
10 21’ N and from 1030 27’ E to 1030 37’ E which cover the area of
international shipping line to shoreline of south west of Johor in
Malaysia. The source of spill is considered from a vessel sailing in
the international shipping line. The spill is 500 m3 crude oil type
Arabian Medium, Amoco at 7 am.
4. RESULTS

.

Oil fate
prediction
Spreadin
g

Oil slick
trajectory

Shoreline
analysis and
protection priority

In hand
equipment &
techniques

Demonstrating
combating
strategies

Tanjunj
Pelepas Port

Booms

Offshore
recovery
strategy

Skimmers

Evaporation

Dispersion

Viscosity

Emulsification

Tanjunj Bin
Power Plant

Pumps

Mangrove

Sorbent
materials
Dispersion
system
Vessels, Barges
, motorized &
manual equipment

Offshore
dispersion
strategy
Shoreline
protection
strategy
Shoreline
recovery &
clean up
strategy
4.1 RESULTS OF OIL FATE PREDICTION

i.
ii.

iii.
iv.
v.

Spreading
Evaporation
Dispersion
Viscosity
Emulsification
4.1.1 SPREADING
9

8

7

6
Wind speed (nm)

5

Major diameter (km *0.5)
4

Minor diameter (km *0.5 )

3

2

1

0
7

8

9

10

11

12

13

14

15

16

17

Prediction of changing of oil slick area from 7 a.m. to 4 pm
4.1.2 EVAPORATION

Predicted quantity of evaporated oil
4.1.3 DISPERSION

Predicted quantity of naturally dispersed oil
4.1.4 VISCOSITY

Predicted change of viscosity of spilled oil
4.1.4 EMULSIFICATION
700

600

500

400
Quantity of oil (m3)
Quantity of emulsion and oil (m3)

300

200

100

0
1

2

3

4

5

6

7

8

9

Hours

Predicted quantity of oil and oil with emulsion within 9 hours
4.2 RESULTS OF OIL SLICK TRAJECTORY PREDICTION
CONT.
4 pm

2 pm

11 am
7am

Predicted trajectory line pointed on each hour
CONT.

4 pm

2 pm

11 am
7 am

Predicted trajectory line by using Google earth
4.3 RESULTS OF SHORELINE ANALYSIS AND PROTECTION PRIORITY

Tanjung Pelepas Port
Tanjung Bin power plant
Mangrove forest (9 km)

High sensitive areas south west of Johor (Google earth)
4.4 RESULTS OF USED EQUIPMENT

Item

Types

Booms

Fence, air inflated and shore sealing

Skimmers

Offshore weir, shallow water weir, oleophilic disk,
vacuuum and toothed disc mechanical skimmers

Pumps

Peristaltic, diaphragm and centrifugal pump

Chemical
dispersant

Two arms on board extended towards port and
starboard

Additional in hand
equipments

Two oil pollution control vessels 20 knots, Three support
vessels, Storage tanks 320 cubic meters, Sorbents
material, manual and motorized equipment
4.5 RESULTS OF DEMONSTRATING COMBATING STRATEGIES
4.5.1 Offshore recovery strategy
4.5.1.1 STAGE ONE
4.5.1.2 STAGE TWO
4.5.2 OFFSHORE DISPERSION STRATEGY
4.5.2.1 STAGE ONE
4.5.2.2 STAGE TWO
4.5.3 SHORELINE PROTECTION STRATEGY
Boo
Length of No. of
m No. booms
anchors
& weight

1

500 m

32 x 35
kg

2

500 m

32 x 35
kg

3

300 m

20 x 35
kg

4

400 m

26 x 35
kg

1
4

3
2

Protection technique for zone 1

Technique type: staggered shervon
.
configuration
CONT.
Boom Length of
No.
boom

No. of
anchors &
weight

1

200 m

0

2

200 m

0

3

70 m

5 x 35 kg

4

20 m

1 x 35 kg

5

1300 m

0

Technique type: staggered
shervon
and exclusive
configuration

Protection technique for Zone
two
4.5.4 SHORELINE RECOVERY AND CLEAN-UP

The remained 300 m3 of oil and emulsion reached
next to tidal zone and might be scattered along the
shoreline and went into part of Johor strait.
The recovery of collected oil in the deployed
protection booms areas depend upon instant
findings and ought to be done by using oleophilic
skimmer, Shore and harbour weir skimmer
, diaphragm pump, Vacuum systems and Sorbent
materials . In addition to manual and motorized
equipment.
4.5.5 RESULT OF COMBATING BASED ON PREDICTION

General budget after offshore combating
CONT.
Operation

Combated oil (m3)

Combated oil and
emulsion (m3)

Offshore recovery
operation (stage one)

74

103

Offshore recovery
operation (stage two)

60

83

Offshore dispersion
operation (stage one)

19

26

Offshore dispersion
operation (stage two)

13

26

Remaining

240

300

 Protection of the most environmental and economical sensitive areas such
as Tanjung Pelepas Port, Tanjung Bin steam power, most of the mangrove
shoreline up to Puteri Habour was based on prediction of the slick
trajectory.
 Large quantity of contaminate was accumulated next to the protection
booms which led to make shoreline clean-up and recovery easier and faster.
5 CONCLUSION


This research simulated an oil fate and slick trajectory predictions for
marine oil pollution control strategies to reach highest environmental and
economical benefit in south east of Johor.



The developed combating strategies flow chart was applied and cover all
the strategies which are used.



The highest sensitive areas in Johor state were nominated to be protected
whenever a significant oil spillage will be happened.



Matrix of equipment, which are suitable of Johor, was listed to deal with
wide range of oil types.



Protection booming configuration to protect the highest sensitive areas was
appointed according to the special geographical area in the south east of
Johor.
PAPERS

Two papers still in processing to be published and entitled :


OIL FATE AND TRAJECTORY SIMULATION IN MALAYSIAN
SHORELINE



OIL POLLUTION COMBATING STRATEGIES SIMULATION
IN MALAYSIAN SHORELINE
Thank you
Trima kaseh

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Oil fate and slick trajectory predictions for oil pollution control combating strategy

  • 1. DEPARTMENT OF MARINE TECHNOLOGY FACULTY OF MECHANICAL ENGINEERING UNIVERSITI TEKNOLOGI MALAYSIA OIL FATE AND SLICK TRAJECTORY PREDICTIONS FOR MARINE OIL POLLUTION CONTROL STRATEGIES (MMK1180) NAME : MATRIC No. : MOHAMMED ALI AL-MUHANDES MM091250 SUPERVISORS : BIN AHMAD MAIN : ASSOC. PROF. DR. ZAMANI CO. : DR. JASWAR
  • 2. 1. INTRODUCTION 1.1 RESEARCH BACKGROUND O’conneli (2006) stated that oil pollution affects on :  Fisheries and aquaculture resources ,  Tourism and,  Costal industries In this research:  It is essential to predict the oil fate and slick trajectory  Combating strategies need to be set  Through simulation
  • 3. 1.2 PROBLEM STATEMENT Oil pollution control strategies need to be developed for each oil fate and slick trajectory scenario. Since each scenario is unique and independent, simulation method is preferred.
  • 4. 1.3 OBJECTIVE To develop a method of choosing oil pollution combating strategies
  • 5. 2. LITERATURE REVIEW i. Oil fate; The most important processes are spreading, evaporation, dispersion viscosity and emulsification (O’connel, 2006c). ii. Slick trajectory; When an oil slick is predicted to affect on high sensitive area, this prediction helps the decision maker significantly to choose the combating strategies. iii. Types of shorelines; according to geographical shape, types of beaches and to the environmental and socio-economic activities (IPIECA 2008a). iv. In-hand equipment and combating strategies; the limitation of spill control techniques must be taken into consideration in determining the most appropriate clean up response (Persga, 2009a). All of on-scene commanders are allowed to take whatever action is appropriate to clean up and/or mitigate the effects of an oil spill (Ch'ng,1997).
  • 6. CONT. 72 references have been used in the thesis
  • 7. 3. RESEARCH METHODOLOGY Determine oil fate and slick trajectory criteria  Determine oil fate and slick trajectory Determine protection priority and types of shorelines Determine equipment and techniques Determine strategy Validation by Case of study
  • 8. 3.1 DETERMINATION OF OIL FATE Item Spreading Evaporation Dispersion Viscosity Emulsification Using method Lehr’s relationships (math. equation) for major and minor diameters of ellipse ADIOS2 (software) ADIOS2 (software) ADIOS2 (software) Mackay’s relationship (math. equation)
  • 9. 3.2 DETERMINATION OIL SLICK TRAJECTORY The oil slick trajectory was calculated using slick trajectory calculator software based on:  Wind effects 3% of its speed in its direction within specific time  Current affects 100% of its speed in its direction within the same specific time
  • 10. 3.3 PROTECTION PRIORITY AND TYPES OF SHORELINES    Biological resources high priority Mangrove Human use features high priority Water intake and port Shorelines high priority Mangrove
  • 11. 3.4 EQUIPMENT AND USED TECHNIQUES Techniques Equipment Containment and protection booming Booms : Fence; Air inflated; Shoreline . . sealing Recovery Skimmers: Weir; Oleophilic; Vacuum; . Mechanical Pumps: Archimedean; Reciprocating; . Peristaltic; Diaphragm; Centrifugal Dispersion spray system mounted on workboat Airplane Helicopter Clean up Sorbents: Inorganic, Natural organic and Synthetic Motorized equipment Manual equipment
  • 12. 3.5 DETERMINE STRATEGY Offshore recovery strategy i.   ii. iii. iv. Skimmers pumps Offshore dispersion strategy Shoreline clean up and recovery strategy Shoreline protection strategy
  • 14. CONT.
  • 15. CONT.
  • 16. 3.5.1 OFFSHORE RECOVERY STRATEGY 3.5.1.1 SKIMMERS
  • 18. 3.5.2 OFFSHORE DISPERSION The applying dispersant according to equations covered the following: Application rate Vdis (litre/hectare) Application rate Qdis (litre/sec) Required speed (knot)
  • 19. 3.5.3 SHORELINE CLEAN UP AND RECOVERY STRATEGY
  • 21. 3.6 CASE OF STUDY The oil spill incident is simulated at area extended from 10 09’ N to 10 21’ N and from 1030 27’ E to 1030 37’ E which cover the area of international shipping line to shoreline of south west of Johor in Malaysia. The source of spill is considered from a vessel sailing in the international shipping line. The spill is 500 m3 crude oil type Arabian Medium, Amoco at 7 am.
  • 22. 4. RESULTS . Oil fate prediction Spreadin g Oil slick trajectory Shoreline analysis and protection priority In hand equipment & techniques Demonstrating combating strategies Tanjunj Pelepas Port Booms Offshore recovery strategy Skimmers Evaporation Dispersion Viscosity Emulsification Tanjunj Bin Power Plant Pumps Mangrove Sorbent materials Dispersion system Vessels, Barges , motorized & manual equipment Offshore dispersion strategy Shoreline protection strategy Shoreline recovery & clean up strategy
  • 23. 4.1 RESULTS OF OIL FATE PREDICTION i. ii. iii. iv. v. Spreading Evaporation Dispersion Viscosity Emulsification
  • 24. 4.1.1 SPREADING 9 8 7 6 Wind speed (nm) 5 Major diameter (km *0.5) 4 Minor diameter (km *0.5 ) 3 2 1 0 7 8 9 10 11 12 13 14 15 16 17 Prediction of changing of oil slick area from 7 a.m. to 4 pm
  • 26. 4.1.3 DISPERSION Predicted quantity of naturally dispersed oil
  • 27. 4.1.4 VISCOSITY Predicted change of viscosity of spilled oil
  • 28. 4.1.4 EMULSIFICATION 700 600 500 400 Quantity of oil (m3) Quantity of emulsion and oil (m3) 300 200 100 0 1 2 3 4 5 6 7 8 9 Hours Predicted quantity of oil and oil with emulsion within 9 hours
  • 29. 4.2 RESULTS OF OIL SLICK TRAJECTORY PREDICTION
  • 30. CONT. 4 pm 2 pm 11 am 7am Predicted trajectory line pointed on each hour
  • 31. CONT. 4 pm 2 pm 11 am 7 am Predicted trajectory line by using Google earth
  • 32. 4.3 RESULTS OF SHORELINE ANALYSIS AND PROTECTION PRIORITY Tanjung Pelepas Port Tanjung Bin power plant Mangrove forest (9 km) High sensitive areas south west of Johor (Google earth)
  • 33. 4.4 RESULTS OF USED EQUIPMENT Item Types Booms Fence, air inflated and shore sealing Skimmers Offshore weir, shallow water weir, oleophilic disk, vacuuum and toothed disc mechanical skimmers Pumps Peristaltic, diaphragm and centrifugal pump Chemical dispersant Two arms on board extended towards port and starboard Additional in hand equipments Two oil pollution control vessels 20 knots, Three support vessels, Storage tanks 320 cubic meters, Sorbents material, manual and motorized equipment
  • 34. 4.5 RESULTS OF DEMONSTRATING COMBATING STRATEGIES 4.5.1 Offshore recovery strategy
  • 40. 4.5.3 SHORELINE PROTECTION STRATEGY Boo Length of No. of m No. booms anchors & weight 1 500 m 32 x 35 kg 2 500 m 32 x 35 kg 3 300 m 20 x 35 kg 4 400 m 26 x 35 kg 1 4 3 2 Protection technique for zone 1 Technique type: staggered shervon . configuration
  • 41. CONT. Boom Length of No. boom No. of anchors & weight 1 200 m 0 2 200 m 0 3 70 m 5 x 35 kg 4 20 m 1 x 35 kg 5 1300 m 0 Technique type: staggered shervon and exclusive configuration Protection technique for Zone two
  • 42. 4.5.4 SHORELINE RECOVERY AND CLEAN-UP The remained 300 m3 of oil and emulsion reached next to tidal zone and might be scattered along the shoreline and went into part of Johor strait. The recovery of collected oil in the deployed protection booms areas depend upon instant findings and ought to be done by using oleophilic skimmer, Shore and harbour weir skimmer , diaphragm pump, Vacuum systems and Sorbent materials . In addition to manual and motorized equipment.
  • 43. 4.5.5 RESULT OF COMBATING BASED ON PREDICTION General budget after offshore combating
  • 44. CONT. Operation Combated oil (m3) Combated oil and emulsion (m3) Offshore recovery operation (stage one) 74 103 Offshore recovery operation (stage two) 60 83 Offshore dispersion operation (stage one) 19 26 Offshore dispersion operation (stage two) 13 26 Remaining 240 300  Protection of the most environmental and economical sensitive areas such as Tanjung Pelepas Port, Tanjung Bin steam power, most of the mangrove shoreline up to Puteri Habour was based on prediction of the slick trajectory.  Large quantity of contaminate was accumulated next to the protection booms which led to make shoreline clean-up and recovery easier and faster.
  • 45. 5 CONCLUSION  This research simulated an oil fate and slick trajectory predictions for marine oil pollution control strategies to reach highest environmental and economical benefit in south east of Johor.  The developed combating strategies flow chart was applied and cover all the strategies which are used.  The highest sensitive areas in Johor state were nominated to be protected whenever a significant oil spillage will be happened.  Matrix of equipment, which are suitable of Johor, was listed to deal with wide range of oil types.  Protection booming configuration to protect the highest sensitive areas was appointed according to the special geographical area in the south east of Johor.
  • 46. PAPERS Two papers still in processing to be published and entitled :  OIL FATE AND TRAJECTORY SIMULATION IN MALAYSIAN SHORELINE  OIL POLLUTION COMBATING STRATEGIES SIMULATION IN MALAYSIAN SHORELINE