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Sediment transport and Coastal erosion Al-Azhar University-Gaza Master Program of Water and Environmental Science

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LOGOSediment transport and Coastal

erosion

Al-Azhar University-Gaza

Master Program of Water and Environmental

Science

Contents

Introduction 1

Study Area2

Materials & Methods3

Results & Discussion4

Conclusions5

2

33

Rosetta Promontory

Mediterranean Sea

Nile River

1900

1964

1971

1988

1990

1991

1996

2000

1900

1964

1971

1988

1990

1991

1996

2000

1900

1964

1971

1988

1990

1991

1996

2000

1

2

3

1. Introduction

Construction of the low Aswan dam in 1902 and the

high Aswan dam in 1964 has almost completely

interrupted the Nile River sediment discharge to the sea

(Inman et al, 1976)

Bardawil lagoon sandbar and Delta continue to act as a

significant source and supplier of sand to Gaza coast

(Inman et al, 1976)

Most sediments coming to Gaza are originally from Nile

River and it is about 350,000 cubic meter annually

(Perlin and Kit, 1999)

4

1. Introduction

5

1. Introduction

Alongshore sediment transport can calculate using the following

expressions:

CERC expression

(1)

Kamphuis expression

(2)

where

Hb = breaking wave height,

mb = seabed slop,

D50 = characteristic rock diameter,

αb = breaking wave angle.

6

1. Introduction

7

Sediment,

m3/year

Duration

(d)

ab

(Deg)

Hb

(m)

a0

(Deg)

Ts

(Sec)

Hs

(m)

Wave

Scenarios

60,74628980.62266.30.5H ≤ 1.0m

73,4046361.46157.11.31.0 < H ≤ 2.0

48,8511082.53178.02.42.0 < H ≤ 3.0

31,0502.793.49188.83.43.0 < H ≤ 4.0

3,0780.334.3259.44.2H > 4.0m

220,000365Total

Annual bulk sediment transport rates for Gaza beach (idku)

1. Introduction

8

Sediment

m3/year

Duration

days

ab

deg)

Hb

m)

a0

deg)

Ts

sec)

Hs

(m)

Wave

Scenarios

- 65,374197.10-325.90.67H ≤ 1.0m

137,138159.86356.511.0 < H ≤ 2.0

- 4,8071.80-137.92.252.0 < H ≤ 3.0

43,0333.32208.83.53.0 < H ≤ 4.0

47,1392.9241.28.83.55H > 4.0m

160,000365Total

Annual bulk sediment transport rates for Gaza beach (Ashdoud)

1. Introduction

9

Sediment transport

Types of sediment transport

The amount of sediment transported along shore 170,000 to

540,000 .(Shoshana G., 2000)

1- Cross shore

1. Introduction

10

Sediment transport

2- Alongshore

1. Introduction

In recent decades, the coast of Gaza has been

plagued by a serious shortage of sand and by erosion11

4

1. Introduction

The coast of Gaza was affected by man-made structures

prior to the fishing harbour (Zviely and Klein, 2003)

In 1972 two groins, 120m long each 500m apart

12

5The erosion was controlled by a series of nine

detached breakwaters built in 1978

The detached

breakwaters, 50-120 m

long, were built 50 m

from the coast line at a

depth of 1 m

1. Introduction

13

6 In 1994, the construction of Gaza fishing harbor started

and completed in 1998. The construction negatively

increase the erosion rates

The fishing

harbor extends

some 500m into

the sea,

enabling access

to vessels up to

6m deep.

1. Introduction

14

2. Study Area

The study covers an area

extended from Wadi Gaza up to

3km north the Gaza fishing

harbour

15

16

Gaza harbor

17

18

3. Materials and Methods

Data were collected from analyses of Landsat

images from 1972 to 2010 and combined with

sample collection for grain size analyses in

order to study the shoreline change

Numerical model runs to predict the

morphodynamics around the mitigation

structures were carried out

19

3.1 Satellite images

Image source DateResolution

[m m]

Landsat 1 MSS 29-06-1972 60.0 60.0

Landsat 5 MSS 14-05-1984 60.0 60.0

Landsat 5 TM 29-05-1998 30.0 30.0

Landsat 5 TM 29-03-2003 30.030.0

Landsat 7 ETM+ 04-06-2010 30.030.0

3. Materials and Methods

The infrared band was selected for

the subsequent image processing.

The image processing procedures

were carried out using ERDAS

Imagine and ArcGIS

20

3.2 Numerical model

The relocation of fishing harbor to offshore,

groins field system, detached breakwaters and

wide-crested submerged breakwaters were

suggested and examined using the

morphodynamic numerical model of nearshore

waves, currents, and sediment transport in order

to mitigate the coastal erosion (Seif et al., 2011)

3. Materials and Methods

21

4. Results and Discussion

Image period

Erosion Accretion

area ×103

[m2]

rate ×103

[m2 year-1]

area ×103

[m2]

rate ×103

[m2 year-1]

1972-1984 180 15 122 10

1984-1998 200 14 224 16

1998-2003 8 2 190 38

2003-2010 143 20 70 10

Total 531 14 606 16

Accretion and erosion rates for the study area

4.1 Remote sensing findings

The impact has extended to about 2.5km

to north and to south the harbor

The waterline advanced at the south of

harbor by 0.75 m year-1 and treated at the

north of harbor by 1.15 m year-1

22

4.2 Sediment transport rates

The net annual rate of wave-induced

alongshore sediment transport range from

minimum 160×103 to maximum 220×103 m3,

and the average annual rate of 190×103 m3,

northward

The sand volume of accretion was estimated

80×103 m3 per year

4. Results and Discussion

23

4.3 Numerical model results

4. Results and Discussion

Offshore fishing harbor

model test

Unit: m

0.2

0.2

0.20.4

0.4

0.4

0.6

0.6

0.60.8

0.8

0.81

1

11.2

1.2

1.21.4

1.4

1.4

1.6 1.6

1.81.8

222.2

2.22.4 2.4

2.6 2.6

2.8 2.8

33.23.43.6

3.84

4.2

0

0

0 0

0

0000

00000

000

0

1000

800

600

400

200

0

0 200 400 600 800 1000

X(m

)

Y(m )

1000

800

600

400

200

0 200 400 600 800 1000

X(m

)

Y(m)

1m/s

-1

0

1

2

34

5 5

6

7

8

5 5

1000

800

600

400

200

0

0 200 400 600 800 1000

X(m

)

Y(m )

Unit: m-1

0

1

2

34

5 5

6

7

8

3

5 5

1000

800

600

400

200

0

0 200 400 600 800 1000

X(m

)

Y(m )

Unit: m

N

N

24

25

4. Results and Discussion

Detached breakwater

model test

0.2 0.20.4 0.4

0.60.811.21.41.61.822.22.42.62.83

3.23.43.6

3.8

4

4.2

0

0

0

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)

Y(m )

Unit: m1m/s

800

600

400

200

0 200 400 600

X(m

)

Y(m)

-1

0

1

2

3

4

5

6

7

8

9

10

11

12

13

1414

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)

Y(m )

Unit: m -1

0

1

2

34

5

6

7

8

9

10

11

12

13

1414

5

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)Y(m )

Unit: m

N4.3 Numerical model results

26

4. Results and Discussion4.3 Numerical model results N

Submerged

breakwaters model

test

0.20.40.60.811.2

1.4

1.4

1.4

0

0

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)

Y(m )

Unit: m

1m/s

800

600

400

200

0 200 400 600

X(m

)

Y(m)

-1

0

1

2

3

45

6

7

8

9

10

11

12

13

1414

32

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)

Y(m )

Unit: m -1

0

12

3

4

5

6

7

8

9

10

11

12

13

1414

32

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)

Y(m )

Unit: m

27

4. Results and Discussion4.3 Numerical model results N

0.20.40.60.811.21.41.61.82

2.22.42.62.83

3.23.43.6

3.8

4

4.2

0

0

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)

Y(m )

Unit: m

1m/s

800

600

400

200

0 200 400 600

X(m

)

Y(m)

-1

0

1

2

3

4

5

6

7

8

9

10

11

12

13

1414

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)

Y(m )

Unit: m -1

012

3

4

5

6

7

8

9

10

11

12

13

1414

800

600

400

200

0

0 100 200 300 400 500 600

X(m

)Y(m )

Unit: m

Groins field system model

test

28

4. Results and Discussion

4.3 Numerical model results

Mitigation alternativeAnnual rate

[m3 km-1]Remarks

Relocation of harbor + 4×103 Accretion

Detached BW ‒23×103 Erosion

Submersed BW +28×103 Accretion

Groins field system ‒22×103 Erosion

Environmental impact of various mitigation alternatives

29

The erosion problem along Gaza beach is due

to the man-made structures as confirmed by

analyzing the historical satellite images from

1972 to 2010

The numerical model results show that the

offshore harbor is the best alternative for Gaza

beach restoration

Alternatively, the wide-crested submerged

breakwater, “artificial reef”, is an effective

structure for preventing sandy beach erosion

5. Conclusions

30

Mazen Abualtayef, Ahmed Abu Foul, Ahmed Khaled Seif, Abdel Fattah Abd

Rabou, Omar Matar, Rashad Alhourani, Samir Matar, and Ibrahim Alshiekh.

Mitigation measures for Gaza caostal erosion. 4th International Engineering

Conference, Islamic University of Gaza, Gaza, Palestine, pp 1-13, October

15-16, 2012

Ahmed Seif. Numerical simulation of 3D morphodynamic around coastal

structures using quasi-3D nearshore current model. Doctorate thesis, Tottori

university, 2011.

Ahmed Seif, Masamitsu Kuroiwa, Mazen Abualtayef, Hajime Mase, Yuhei

Matsubara. A hydrodynamic model of nearshore waves and wave-induced

currents. Inter. J. Nav. Archit. Oc. Engng, 3(3), 216-224, 2011.

Burcharth H, Hawkins S, Zanuttigh B, Lamberti A. Environmental design

guidelines for low crested coastal structures, 2007.

Lee E. Harris, Ph.D., P.E. Investigations and recommendations for solutions

to the beach erosion problems in the city of Herzliya, Israel, 2007.

References

31

Dov Zviely and Micha Klein. The environmental impact of the Gaza Strip

coastal constructions. Journal of coastal research, 19(4), 1122-1127, 2003.

M. A. Azab and A. M. Noor. Change detection of the North Sinai coast by

using remote sensing and geographic information system, 2003.

Palestinian National Authority, Ministry of Environmental affairs. Gaza Coastal

and Marine Environmental Protection and Management Action Plan, 2000.

References

32

LOGO

33

[email protected]