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EXPERIMENTAL STUDY ON THE EFFECT OF SUBMERGED BREAKWATER CONFIGURATION ON LONG WAVE RUN-UP REDUCTION
A THESIS SUBMITTED TO THE GRADUATE DIVISION OF THE UNIVERSITY OF HAWAII AT MANOA IN PARTIAL FULFILLMENT OF
THE REQUIREMENTS FOR THE DEGREE OF
MASTER OF SCIENCE
IN
CIVIL ENGINEERING
December 2014
By
Tony K.C. Shing
Thesis Committee:
Michelle H. Teng, Chairperson
Oceana Francis
Ian N. Robertson
1
Abstract
Experimental study was carried out to observe and quantify the effects that a submerged
breakwater has on long wave run-up reduction. As shown in the past, long wave run-up, or
tsunami can be very devastating. In 2011, the tsunami in Japan resulted in over 300 billion
dollars of damages along with several thousand lives. A recent finding of coral and ocean
sediments found in a sinkhole in Kauai suggest that this catastrophic event could happen in
Hawaii. The focus of this thesis study is to find the optimal breakwater length for run-up
reduction and examine the effects that a breakwater’s geometry has on run-up reduction, aiming
at seeking specific configurations and designs of submerged breakwater that may be effective in
reducing long wave run-up. This included experimental test on waves of different amplitude (up
to 10 different amplitude) propagating over breakwater models of different material
(rigid/impermeable/smooth surface vs. flexible/porous/rough surface), length, spacing, and
geometry, and running-up onto artificial beach of different slopes. In addition, the experimental
results were compared with a previous numerical study done by Mohandie (2008) and Mohandie
and Teng (2012). In their numerical study, it was found that when the length of a submerged
rectangular breakwater is twice the wavelength of the generated long wave, the maximum run-up
reduction rate was achieved. This numerical result had not been examined and validated in an
experiment before this thesis study.
In the present thesis study, it was found that foam/flexible breakwater material provided a
better run-up reduction than plastic/rigid material. For the effect of the geometry of the
breakwater, a triangular saw-tooth geometry provided better run-up reduction than a circular
speed bump geometry. Both triangular and circular models provided better run-up reduction
2
than a flat rectangular model. For the effect of breakwater length, the experimental results
generally follow the same trend as the numerical simulations done by Mohandie and Teng (2012).
The results showed a trend of increasing run-up reduction until a certain point before decreasing
as the model length increases. The point at which the run-up reduction decreases varied in the
experimental results and ranged from 1.25-1.9 wavelengths. In the 5 degree beach slope test,
two rectangular breakwater models with a spacing in-between compared to a breakwater models
of equal length without the spacing showed no significant difference in run-up reduction.
However, in the 10 degree beach slope test, the results were mixed. The rigid rectangular model
had a better run-up reduction for the breakwater model with spacing whereas the flexible
rectangular model had a better run-up reduction for the breakwater without spacing. This issue
may require further investigation.
The results from this study may be useful in future design of submerged breakwaters for
reducing long wave run-up. Specifically, we recommend breakwaters with a saw-tooth geometry,
or of flexible/porous material with a rough surface. For the breakwater length, it should be
comparable to the wavelength, if practically possible in near shore regions.
3
Acknowledgment
I would like to thank Professor Michelle H. Teng, for her dedication and support
throughout the years. Without her, I would not have started my master studies, much less finish
it. I am grateful for Professor Oceana Francis and Ian N. Robertson for their advice and
willingness to help. I want to thank the CEE department for offering me teaching assistantship
and scholarships during my graduate studies. Besides the financial support, the teaching
assistantship was a great experience. I am thankful for Thi Hong Vo for helping me along the
way and for volunteering her time to help me with the experiments. I am thankful for Ame
Arakaki for all her help and for her assistance with the models. I would also like to thank our
summer interns Kap’a Akau and Selena Torres for their valuable input in this master thesis. I
would like to thank Board of Water Supply and my supervisors Ann Wong and Lyann Okada for
being supportive and flexible throughout my master’s studies. Lastly, I would like to thank my
family and friends for always being there.
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Table of Contents
Abstract ........................................................................................................................................... 2
Acknowledgment ........................................................................................................................ 4
CHAPTER 1 INTRODUCTION ........................................................................................... 13
1.1 Technical Background.................................................................................................... 13
1.2 Literature Review ........................................................................................................... 14
1.3 Objective of Present Study ............................................................................................. 15
CHAPTER 2 THEORY, GOVERNING EQUATIONS AND EXISTING NUMERICAL
RESULTS 16
2.1 Governing Equations for Long Wave Propagation ........................................................ 16
2.2 Governing Equation for Long Wave Run Up ................................................................ 17
2.3 A Solitary Wave as the Initial Wave .............................................................................. 18
2.4 Existing Numerical Results ............................................................................................ 19
CHAPTER 3 EXPERIMENTAL DESIGN, SETUP AND MEASUREMENTS ................. 22
3.1 Wave Flume and Wave Generation ............................................................................... 23
3.2 Description of the Wavemaker ....................................................................................... 26
3.3 Artificial Beach .............................................................................................................. 27
3.4 Measurement of Wave Height and Run-Up ................................................................... 28
3.5 Breakwater Model Set-Up .............................................................................................. 29
3.5.1 Rectangular foam and plastic model set-up.................................................... 31
3.5.2 PVC models:angle and semi-circular models ................................................ 32
CHAPTER 4 EXPERIMENTAL RESULTS ........................................................................ 34
5
4.1 Reference Case ............................................................................................................... 34
4.2 Plastic Rectangular Model ............................................................................................. 36
4.3 Rectangular Foam Model ............................................................................................... 40
4.4 PVC Saw-Tooth Shaped Angle Model .......................................................................... 44
4.5 PVC Semi-Circular Continuous Bump Model ............................................................... 46
CHAPTER 5 ANALYSIS AND DISCUSSION ................................................................... 48
5.1 Rectangular Model Comparison, Foam Vs Plastic ........................................................ 48
5.1-1 Run-up vs. wave amplitude on beach with 5 degree slope ............................ 48
5.1-2 Effect of model length on run-up reduction for 5 degree beach .................... 51
5.1-3 Run-up vs. wave amplitude on beach with 10 degree slope .......................... 54
5.1-4 Effect of model length on run-up reduction for 10 degree beach .................. 57
5.2 PVC Model Comparison: Angle vs Semi-Circular ........................................................ 60
5.3 PVC model vs. Rectangular Models .............................................................................. 65
5.4 Experimental Plastic Rectangular Model vs. Mohandie’s (2008) Numerical Results
Regarding Optimal Breakwater Length .................................................................................... 68
5.5 Rectangular Models 5 ft Breakwater Spacing Configuration ....................................... 71
5.6 Errors and Accuracies .................................................................................................... 77
CHAPTER 6 Conclusion ....................................................................................................... 78
6.1 Summary of work and findings ...................................................................................... 78
6.2 Recommendations .......................................................................................................... 80
REFERENCES .......................................................................................................................... 82
6
Table of Figures
Figure 2.1-1: Sketch of wave propagation over a submerged breakwater and run-up on a beach 16
Figure 2.4-1: Existing numerical results on the effect of breakwater length on run-up reduction
(Mohandie 2008). .......................................................................................................................... 21
Figure 3.1-1: Experimental Setup Sketch ..................................................................................... 23
Figure 3.1-2: Experimental setup in the lab, blue is the wave gauge, red is the wavemaker,
orange is the end of the beach slope with angle measurer, and green is the ruler to measure water
depth before each trial ................................................................................................................... 24
Figure 3.3-1: Photo of beach set-up .............................................................................................. 27
Figure 3.3-2: Photo of beach set-up at 10 degrees with angle measurement ................................ 27
Figure 3.4-1: Photo of wave gauge set-up in the lab ................................................................... 29
Figure 3.5.1-3.5.1-1: Comparison of foam and plastic rectangular models ................................. 31
Figure 3.5.1-2: Height comparison of the foam model and plastic model in the flume .............. 32
Figure 3.5.2-3.5.2-1: Full length of the PVC and angle models. The legnth of both models is
about equal. However, there are only 12 humps for the angle model vs. 16 for the semi-circular
PVC model. ................................................................................................................................... 33
Figure 3.5.2-3.5.2-2: Height comparison of the semi-circular PVC and angle models ................ 33
Figure 5.1-1-1: Run-up of a solitary wave on 5 degree beach after propagating over a plastic
rectangular breakwater model. ...................................................................................................... 49
Figure 5.1-1-2: Run-up of a solitary wave on 5 degree beach after propagating over a foam
rectangular breakwater model. ...................................................................................................... 49
Figure 5.1-1-3: Plastic vs. Foam Run-up at 5 degree, L=5 ft ....................................................... 50
7
Figure 5.1-1-4: Plastic vs. Foam Run-up at 5 degree, L =10 ft .................................................... 51
Figure 5.1-2-1: Plot of run-up reduction vs. the ratio of breakwater model length over
wavelength for α around 0.17; green triangles: plastic rectangular model, red squares: foam
rectangular model.......................................................................................................................... 52
Figure 5.1-2-2: Plot of run-up reduction vs. the ratio of breakwater model length over
wavelength for α around 0.22; green triangles: plastic rectangular model, red squares: foam
rectangular model.......................................................................................................................... 53
Figure 5.1-2-3: Plot of run-up reduction vs. the ratio of breakwater model length over
wavelength for α around 0.25; green triangles: plastic rectangular model, red squares: foam
rectangular model.......................................................................................................................... 53
Figure 5.1-3-1: Run-up of a solitary wave on 10 degree beach after propagating over a plastic
rectangular breakwater model. ...................................................................................................... 54
Figure 5.1-3-2: Run-up of a solitary wave on 10 degree beach after propagating over a foam
rectangular breakwater model. ...................................................................................................... 55
Figure 5.1-3-3: Plastic vs. Foam Run-up at 10 degree, 5 ft L ....................................................... 56
Figure 5.1-3-4: Plastic vs. Foam Run-up at 5 degree, 10 ft L....................................................... 56
Figure 5.1-4-1: Plot of run-up reduction vs. the ratio of breakwater model length over
wavelength for α around 0.11; green triangles: plastic rectangular model, red squares: foam
rectangular model.......................................................................................................................... 57
Figure 5.1-4-2: Plot of run-up reduction vs. the ratio of breakwater model length over
wavelength for α around 0.14; green triangles: plastic rectangular model, red squares: foam
rectangular model.......................................................................................................................... 58
8
Figure 5.1-4-3: Plot of run-up reduction vs. the ratio of breakwater model length over
wavelength for α around 0.26; green triangles: plastic rectangular model, red squares: foam
rectangular model.......................................................................................................................... 58
Figure 5.1-4-4: Model length vs. run-up reduction for 10 degree beach – smaller amplitudes .... 59
Figure 5.2-1: Comparison of PVC models: Circular vs. Angle on 10 degree beach .................... 60
Figure 5.2-2: Comparison of PVC models: Circular vs. Angle on 10 degree beach .................... 61
Figure 5.2-3: PVC Model, Run-up Reduction Normalized by Model Height 5 degree ............... 63
Figure 5.2-4: PVC Model, Run-up Reduction Normalized by Model Height 10 degree ............. 63
Figure 5.3-1:Experimental Results from Mohandie (2007); Rectangular Rigid model 5 degree
slope; d/h of 0.65........................................................................................................................... 66
Figure 5.3-2: Experimental results PVC model run-up; 5 degree slope ....................................... 67
Figure 5.4-1: Numerical vs. Experimental Results Plastic Rectangular Models .......................... 68
Figure 5.4-2: Numerical vs. Experimental Results Foam Model ................................................. 69
Figure 5.5-1: Normal Experimental Setup with 5 ft model used for comparison......................... 71
Figure 5.5-2: Experimental Setup of breakwater model with spacing .......................................... 72
Figure 5.5-3: Plastic Model with spacing comparisons 5 degree ................................................. 75
Figure 5.5-4: Foam Model with spacing comparison 5 degree .................................................... 75
Figure 5.5-5: Plastic Model with spacing comparisons 10 degree ............................................... 76
Figure 5.5-6: Plastic Model with spacing comparisons 10 degree ............................................... 76
9
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Table of Tables
Table 2.4-1: Effect of reef length L on reducing wave run-up R for d/h of 0.3 ........................... 20
Table 3.2-1: Sample Calibration Results for the Wavemaker ...................................................... 26
Table 4.1-1: Reference case, 5 degree beach slope ...................................................................... 35
Table 4.1-2: Reference case, 10 degree beach slope .................................................................... 35
Table 4.2-1: Plastic Rectangular Model, L = 2.5 ft, 5 degree slope ............................................. 36
Table 4.2-2: Plastic Rectangular Model, L = 5 ft, 5 degree slope ................................................ 36
Table 4.2-3: Plastic Rectangular Model, L = 7.5 ft, 5 degree slope ............................................. 37
Table 4.2-4: Plastic Rectangular Model, L = 10 ft, 5 degree slope .............................................. 37
Table 4.2-5: Plastic Rectangular Model, L = 2.5 ft, 10 degree slope ........................................... 38
Table 4.2-6: Plastic Rectangular Model, L = 5 ft, 10 degree slope .............................................. 38
Table 4.2-7: Plastic Rectangular Model, L = 7.5 ft, 10 degree slope ........................................... 39
Table 4.2-8: Plastic Rectangular Model, L = 10 ft, 10 degree slope ............................................ 39
Table 4.3-1: Rectangular Foam Model, L = 2.5 ft, 5 degree slope ............................................... 40
Table 4.3-2: Rectangular Foam Model, L = 5 ft, 5 degree slope .................................................. 40
Table 4.3-3: Rectangular Foam Model, L = 7.5 ft, 5 degree slope .............................................. 41
Table 4.3-4: Rectangular Foam Model, L = 10 ft, 5 degree slope ................................................ 41
Table 4.3-5: Rectangular Foam Model, L = 2.5 ft, 10 degree slope ............................................. 42
Table 4.3-6: Rectangular Foam Model, L = 5 ft, 10 degree slope ................................................ 42
Table 4.3-7: Rectangular Foam Model, L = 7.5 ft, 10 degree slope ............................................. 43
Table 4.3-8: Rectangular Foam Model, L = 10 ft, 10 degree slope .............................................. 43
Table 4.4-1: PVC Angle Model, L1, 5 degree slope ..................................................................... 44
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Table 4.4-2: PVC Angle Model, L2, 5 degree slope ..................................................................... 44
Table 4.4-3: PVC Angle Model, L1, 10 degree slope ................................................................... 45
Table 4.4-4: PVC Angle Model, L2, 10 degree slope ................................................................... 45
Table 4.5-1: PVC Circular Model, L3, 5 degree slope .................................................................. 46
Table 4.5-2: PVC Circular Model, L4, 5 degree slope .................................................................. 46
Table 4.5-3: PVC Circular Model, L3, 10 degree slope ................................................................ 47
Table 4.5-4: PVC Circular Model, L4, 10 degree slope ................................................................ 47
Table 5.2-1:Run-up Reduction for all four PVC model setup 5 degree ....................................... 62
Table 5.2-2: Run-up Reduction for all four PVC model setup 10 degree .................................... 62
Table 5.4-1: Optimal Model Length based on Rectangular Plastic Models ................................. 69
Table 5.4-2: Run-up Reduction for PVC Models ......................................................................... 70
Table 5.4-3 Run-up Reduction for PVC Models .......................................................................... 71
Table 5.5-1: Plastic Rectangle 5 ft with spacing (5 ft) 5 degree ................................................... 72
Table 5.5-2: Plastic Rectangle 5 ft with spacing (5 ft) 10 degree ................................................. 73
Table 5.5-3: Foam Rectangle 5 ft with spacing (5 ft) 5 degree .................................................... 73
Table 5.5-4: Foam Rectangle 5 ft with spacing (5 ft) 5 degree .................................................... 74
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CHAPTER 1 INTRODUCTION
1.1 Technical Background
A long tidal sea wave, commonly known as a tsunami, is caused by a massive
displacement of water often as a result of an earthquake, landslide or volcanic eruption. The
abrupt change in land mass creates a violent push on the ocean, creating tsunami waves that can
travel in deep ocean as fast as a commercial jet. As the wave approaches shallow water near the
coastline, the speed of the wave decreases, but the amplitude, or height of the wave increases.
The tsunami wave, lasting for hours, can cause major damage to coastal communities. In 2004,
the Indian Ocean tsunami and in 2011, the tsunami in Japan have both created a great deal of
damage wiping out almost everything in its vicinity. Locally in Hawaii, the 2011 tsunami was
of a smaller scale. The long travel time of the tsunami from Japan to Hawaii also allowed time
for evacuation in Hawaii if needed. However, the 2011 tsunami still incurred a significant
amount of damage in Hawaii. According to the state’s estimate, the tsunami damage totaled
$30.6 million (Hawaii 24/7). However, a later FEMA report estimated the damage total at $6.2
million (Insurance Journal), and a congressional research service report stated the damage at
“tens of millions of dollars” (Nanto 2011). The disaster preparedness and tsunami warning
systems are working and are saving lives, but more can be done. The aftermath of any tsunami is
often the rebuilding of lost homes, and shattered businesses. Rather than just a warning system,
the tsunami itself needs to be mitigated, if possible.
Areas prone to tsunami, such as Japan, have built breakwaters, which are natural or man-
made structures used to mitigate the tsunami wave by either stopping the wave or absorbing the
impact/energy of the wave. Commonly used breakwaters are above water, also known as
seawalls. In Japan, about 40% of the coast have seawalls – these are extremely important as
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areas near the epicenter of the earthquake have little to no time to evacuate. In the 2011 tsunami
in Japan, the first tsunami wave hit the coast in less than 30 minutes after the earthquake. With
such little time to evacuate, it is important to have an effective tsunami mitigation in place.
Underwater breakwaters, in combination with other tsunami mitigation methods, could help
reduce the damage of the tsunami waves.
1.2 Literature Review
Many studies have been conducted on tsunamis, and on breakwaters and reefs as
potential mitigating measures against tsunamis. To list a few, Liu, Cho, Briggs, Synolakis and
Kanoglu (1995) carried out a joint numerical and experimental study on solitary wave run-up on
conical island. They found that the leeward side the island can actually experience a larger
tsunami wave height than the windward side due to long waves wrapping around the island.
Chang and Liou (2007) studied the transmission and reflection of tsunami on submerged
trapezoidal breakwater using the matching method based on the linear wave equations, i.e., first
separate the flow domain into different regions, and then solve for the analytical solution for
each region with matching conditions at the interface between two neighboring regions. In their
analytical study, they found that the top plane width (i.e., the top plane length along the wave
propagation direction) of the breakwater plays a major role in wave reflection. Mohandie (2008,
2012) investigated the effects of vegetation and submerged reef/breakwater in reducing long-
wave run-up by using both numerical stimulations and experimental study. He found through
numerical simulation that when the length of a submerged rectangular breakwater or reef is twice
the wavelength, it has the maximum reduction rate on run-up. However, this particular numerical
result was not studied or verified in the wave tank experiments in Mohandie’s research (2008,
2012). Shimabuku (2012) examined the effect of lagoon spacing on run-up reduction and
14
submerged breakwater. Each study’s focus was different, but all studies showed that submerged
breakwaters and reefs are effective in run-up reduction to a certain degree. In both Mohandie
and Shimabuku’s study, the shape of the breakwater was rectangular. The effect of the geometry
and material properties of the breakwater were not investigated.
1.3 Objective of Present Study
The objectives of the present study are:
1) to better understand the interaction between long waves and submerged structures with
different geometry and material properties;
2) to verify the numerical result that an optimal breakwater length exists and that the
optimal length of the breakwater is two times the wavelength by comparing with the
experimental data gathered in this study;
3) to seek optimal configuration and material of submerged breakwaters that can help to
reduce long wave run-up more effectively.
15
CHAPTER 2 THEORY, GOVERNING EQUATIONS AND EXISTING
NUMERICAL RESULTS
In this chapter, the theory and equations that can be used to mathematically model the
long wave propagation and run-up are described briefly. More detailed description can be found
in Mohandie (2008) and Shimabuku (2012).
2.1 Governing Equations for Long Wave Propagation
Figure 2.1-1 shows a sketch of the physical set-up for the problem of interest for this
thesis study. ho is the still water depth, a is the amplitude of the generated wave, ζ is the wave
height, h is the water depth, L is the length of the submerged breakwater, d is the height of the
submerged breakwater, β is the beach slope, and R is the run-up.
The Boussinesq wave model provides a good approximation of non-linear and dispersive
long waves. Since our present experimental study is for waves travelling in a narrow rectangular
channel, a one-dimensional Boussinesq equation can be used to model the waves. The continuity
equation and momentum equation for long wave propagation on smooth bed based on the
Boussinesq model are as follows:
a
ho h
h
ζ
R
L
d breakwater β
x
Figure 2.1-1: Sketch of wave propagation over a submerged breakwater and run-up on a beach
16
( )[ ] 0=++ xt uh ζζ (2.1)
031 2 =−++ xxtxxt uhuuu ζ (2.2)
where ζ is the water surface elevation, u the depth-averaged velocity in the x-direction, h the still
water depth, and t time, suffices represent partial derivatives with respect to that variable.
The variables in equations (2.1) and (2.2) are non-dimensionalized with the constant still
water depth 0h as follows:
,*
0hζζ = ,*
0hxx =
ght
chtt
00
0
**== ,
0
*cuu = (2.3)
where g is gravitational acceleration, 00 ghc = is the linear long wave speed, and * represents
dimensional variables.
2.2 Governing Equation for Long Wave Run Up
During wave run-up, the water depth decreases rapidly, therefore the non-linear effect is
prominent, and the dispersive effect can be ignored. The classical nonlinear and non-dispersive
shallow water equations can be used to model long wave run-up. These equations are:
0=∂∂
+∂∂
xQ
tζ
(2.4)
17
02
=∂∂
+
∂∂
+∂∂
xH
HQ
xtQ ζ (2.5)
where H = h + ζ and Q = uH.
Equation (2.4) and equation (2.5) are equivalent to equation (2.1) and equation (2.2)
without the dispersive factor.
2.3 A Solitary Wave as the Initial Wave
A solitary wave is a single displacement of water above the sea-level and is often used to
model a long wave such as a tsunami in academic research. A mathematical description of the
solitary wave is given by Eqn 2.6 based on the Boussinesq solution (Teng and Wu 1992, Teng
1997):
( ) ( )[ ]( )[ ]ctxxk
ctxxkhtxo
o
−−+−−
= 2
2
tanh1sec,α
αζ (2.6)
where ( )αα
68.0143
+=k , wave speed
( )( ) ( ) ( )[ ]ααα
ααα
−+++
+= 1ln1
2316
2
2
c , and normalized
wave amplitude ha
=α . The wave amplitude can also be related to the effective wavelength as
follows:
( )( )
+−
++=
21
21
1
01.0199.01
01.0199.01
ln1
α
αλke (2.7)
18
( )( )
+−
++=
21
21
5
05.0195.01
05.0195.01
ln1
α
αλke (2.8)
where λe1 and λe5 represent the wavelength between the locations where the water surface
elevation is equal to 1% and 5% of the wave amplitude, respectively. This can also be expressed
as For this study, λe1 was used.
2.4 Existing Numerical Results
The above long wave equations were solved numerically in two previous studies from
our research group (Mohandie 2008 and Shimabuku 2012) to simulate long wave propagation
over submerged reef and breakwaters as shown in Figure 2.1-1. One of the interesting results
from Mohandie (2008)’s numerical simulation was that the length of the submerged breakwater
was found to play a role in reducing the final long wave run-up on a beach. First, it was observed
that if the submerged object is too short, it will not have a significant effect on reducing the run-
up of a long wave. On the other hand, it was also discovered that the reduction effect does not
increase with the length infinitely. Instead, the numerical results showed that there was an
optimal length that would lead to the maximum run-up reduction possible. The specific results
for a sample case with reef height d/ho = 0.3 (normalized breakwater height) and the beach angle
β = 5o were summarized in a later paper (Mohandie and Teng 2012) and also presented in Table
2.4-1 and Figure 2.4-1 here:
19
Table 2.4-1: Effect of reef length L on reducing wave run-up R for d/h of 0.3
initial amplitude α wavelength λ reef length L/λ run-up reduction % 0.1 22.2 0.5 21 0.75 22 1 28 2 32 3 28 0.2 16.0 0.5 15 0.75 20 1 20 2 25 3 24
20
Numerical Results
0
5
10
15
20
25
30
35
0 0.5 1 1.5 2 2.5 3 3.5
model length/wavelength
% re
duct
ion
in ru
n-up
α = 0.1
α = 0.2
Figure 2.4-1: Existing numerical results on the effect of breakwater length on run-up reduction for d/h of 0.30 (Mohandie 2008).
These results indicated that short reefs are less effective than the long reefs in reducing
the wave run-up. However, as the reef length increases beyond twice the wavelength, the
reduction rate starts to drop again. The results showed that when the reef length is approximately
twice the wavelength, the run-up reduction is maximized. The averaged observed reduction rate
due to wave propagating over the submerged breakwaters is roughly 24%. Note that this is for a
case with breakwater height d/ho = 0.3, namely, the breakwater height is 30% of the water depth.
Based on past work, if the breakwater height d is increased, then the reduction rate for run-up
would be higher.
The above numerical results have not been validated by experiments. In addition, in the
numerical studies, only rectangular submerged breakwater models were considered. The reason
is that the numerical models can only simulate submerged bodies with relatively simple
21
geometries and smooth surfaces. Other shapes were not considered since significantly irregular
shapes with abrupt variations can cause the numerical schemes to become unstable. In actual
engineering applications, beyond simple geometries, we are also interested in examining whether
submerged breakwaters with complex geometries, such as those with saw-tooth shaped surface
shapes, would be more effective in reducing wave run-up. Also, besides smooth and rigid surface
materials, we are interested in investigating whether sponge-type of surface material may lead to
more reduction in run-up. These complex cases are difficult to model theoretically or
numerically, and require wave tank experiments to study them.
The objectives of the present study are to carry out wave tank experiments to validate the
numerical results obtained and presented in Mohandie (2008) and Mohandie and Teng (2012),
and to examine submerged breakwater models of complex geometry and different surface
materials in order to seek the most effective design for reducing long wave run-up on a beach.
CHAPTER 3 EXPERIMENTAL DESIGN, SETUP AND MEASUREMENTS
As stated in the earlier sections, the main focus of the present study is to perform wave
tank experiments in order to further investigate the phenomenon of long waves propagating over
submerged breakwater or reefs and examine how the submerged structures would reduce the
wave run-up on dryland. While theoretical modeling and numerical simulations have the
advantage of studying a large number of cases without much material cost such as constructing
physical models and purchasing supplies, they do have limitations. For example, most of the
wave theories are based on certain assumptions, and numerical schemes all have accuracy and
instability issues. They can study cases with simple geometries but may encounter difficulties
modeling complex structures. Because of these, lab experiments remain as a very valuable tool to
22
investigate various fluid and wave phenomena. The dominant methodology used in this study is
lab experiments. In this chapter, the detailed experimental set-up, model construction, and
measurement instruments are described.
3.1 Wave Flume and Wave Generation
The experiments were conducted in a transparent wave flume with dimensions of 6 in
width, 1.25 ft depth, and 35 ft length. Wave generation is done by a wavemaker at one end of
the flume. Figure 3.1-1 illustrates a solitary wave of amplitude α being created in still water of
depth ho with a breakwater model of height d and length L. The angle β is the angle of the
artificial beach, and R is the wave run-up. Symbols WG2 and WG1 represent the wave gauges.
Figure 3.1-2 shows a photo of the experimental setup in the lab.
In this study, the angle of the beach was set at 5 degrees and 10 degrees. Four different
breakwater models each with varying lengths were tested (refer to model setup). The wave
gauges were set upstream and downstream of the breakwater model. A computer program was
used to generate a single solitary wave from the wave maker. Figure 3.1-3 shows the wavemaker
R
L
d breakwater model β
x
WG1 WG2
a
h0
wavemaker
Figure 3.1-1: Experimental Setup Sketch
23
setup. The amplitudes entered into the program starts from 0.05h0 to 0.275 h0 with increments of
0.025 h0. Wave gauge 1 was intended to measure the actual amplitude created by the wavemaker
upstream of the breakwater model.
Figure 3.1-2: Experimental setup in the lab, blue is the wave gauge, red is the wavemaker, orange is the end of the beach slope with angle measurer, and green is the ruler to measure
water depth before each trial
24
Figure 3.1-3: Photo of the wavemaker setup
Figure 3.1-4: Photo of the flume with wavemaker generating periodic waves
25
3.2 Description of the Wavemaker
The wavemaker used in this study was designed and built by a former ORE Ph.D. student
Richard Carter. The wavemaker is a computer controlled piston-type wavemaker. It can generate
periodic waves (Figure 3.1-4), solitary waves or any other waves that the user would like by
inputting the correct wave data in the computer.
While the wavemaker is an excellent tool in performing wave tank experiments, the
generated wave amplitude and period should be measured by a wave gage because in some cases,
the generated wave height and period do not match the input data completely. As an example, the
following calibration results in Table 3.2-1 give us an idea about the accuracy of the wavemaker
for periodic waves:
Table 3.2-1: Sample Calibration Results for the Wavemaker
Input
wave amplitude (in)
Generated
wave amplitude (in)
Input
wave period (sec)
Generated
wave period (sec)
Case 1 0.5 0.35 0.5 0.45
Case 2 1 0.92 1 1
For solitary waves, the wavemaker has a similar level of accuracy for the wave amplitude
and wave form.
26
3.3 Artificial Beach
The beach model was constructed by a plane plexi-glass board braced with uni-struts and
rested near one end of the flume. The setup was made such that the angle of the beach β is
adjustable. Figures 3.3.-1 and 3.3-2 show the beach set-up in the experiments.
Figure 3.3-1: Photo of beach set-up
Figure 3.3-2: Photo of beach set-up at 10 degrees with angle measurement
27
3.4 Measurement of Wave Height and Run-Up
To measure the wave height in this study, two capacitance – type wave gauges were used,
one upstream of the breakwater and one downstream of the breakwater. The first gauge
measured the initial wave amplitude, and the second gauge measured the effects of the
breakwater on the wave over time. The wave gauges were made by a Japanese company JFE
Advantech Co. (Model ACH-600RS). There are a total of three gages available in our hydraulics
lab. We have performed tests to examine the accuracy of the three commercialized gauges.
Specifically, we used the gauges to measure the static water depth in a wave tank at different
depth levels. Then we compared the gauge readings with the depth measured by a ruler. The
results from the two measurement techniques matched with each other closely. The relative
difference was 1.5%, 4.7%, 1.3% for wave gage #1, 2 and 3, respectively.
Wave inundation (D) on the beach shown in Figure 3.1-1 was measured manually by
marking the highest point that the wave reaches on the artificial beach. Then a measuring tape
was used to measure the distance from the still waterline to the marked point. Run-up R was
then calculated using the following relationship R = D sin β. Figure 3.4-1 shows the wave gauge
setup.
28
Figure 3.4-1: Photo of wave gauge set-up in the lab
3.5 Breakwater Model Set-Up
In this study, the main focus is to determine the optimal configuration of a submerged
breakwater for effective run-up reduction. The three factors that were examined are the
breakwater length and the breakwater geometry and material properties. In the two previous
studies conducted by Ravi Mohandie (2008) and Nathan Shimabuku (2012), different conditions
were tested and different results were obtained regarding the optimal breakwater length.
Mohandie found through numerical simulations that the optimal breakwater length was twice the
wavelength. However, Shimabuku’s experimental conditions did not include a breakwater
model as long as twice the wavelength and therefore Mohandie’s findings have not been tested
and verified by experiments. Moreover, in both of those studies only a rectangular breakwater
29
model was used. For this study, four new cases were investigated in order to achieve the
following:
1) test and verify the proposed optimal breakwater length being twice the wavelength
by performing wave flume experiments;
2) test and observe the effects that different geometry and material property of
breakwater has on run-up reduction;
3) based on the experimental results from this study, make recommendations for
optimal breakwater geometry that can be more effective in reducing wave run-up on
coastal land.
30
3.5.1 Rectangular foam and plastic model set-up
Multiple plastic rectangular breakwater models were tested in this study. Their length
was 2.5 ft, 5 ft, 7.5 ft and 10 ft. The height d of the models was 1 inch. The width of the model
encompasses the entire flume width at 6 inches. The water depth h in the experiments was 3
5/16 in, resulting in a relative breakwater height of d/h = 0.30, which matches with the value for
this parameter in Mohandie’s (2008) numerical study. The wave amplitude in the present study
was varied in different testing cases. We note from eqn (2.7) that the wavelength of a solitary
wave is related to the wave amplitude. Specifically, the higher the wave amplitude, the shorter
the wavelength. The four different model lengths paired with ten different wave amplitudes
provided a set of experimental data where the length of the model is less than one wavelength of
the wave, between one and two times the wavelength, and greater than two times the wave
length. In addition, porous foam models with the same geometry of the plastic rectangular
models were tested. To keep the foam models from floating, a thin aluminum plate was glued to
the bottom of the foam models.
Figure 3.5.1-1: Photo comparison of foam (top and bottom) and plastic (middle) rectangular models
31
Figure 3.5.1-2: Photo of height comparison of the foam model and plastic model in the
flume, the foam model is on the left and the plastic model is on the right
3.5.2 PVC models:angle and semi-circular models
In addition to the rectangular models, two “speed bump” variant models with PVC semi-
circles and angles were constructed. Figure 3.5.2-1 shows the full length of the model. The two
models are made to be similar to each other, but due to material constraints, there are slight
differences. The height of the semi-circular model is 1.22 in or 3.2 cm whereas the height of the
angle is 1.77 in or 4.5 cm as shown in Figure 3.5.2-2. The periodic semi-circular PVC model has
16 humps whereas the angle model has 12 humps. Two lengths of the model were tested (i.e., at
full length and half length). The full length of the PVC semi-circular model is about 37 in or 94
cm, whereas the full length of the angle model is 39.4 in or 100 cm. The water depth was 3 5/16
in or 8.4 cm.
32
Figure 3.5.2-1: Full length of the PVC and angle models. The legnth of both models is about equal. However, there are only 12 humps for the angle model vs. 16 for the semi-
circular PVC model.
Figure 3.5.2-2: Height comparison of the semi-circular PVC and angle models
33
CHAPTER 4 EXPERIMENTAL RESULTS
In this study, a large number of wave tank experiments were carried out to investigate the
effect of different types of submerged breakwater models on long wave run-up reduction. In
order to establish a base case or reference case for comparison purposes, the first test we run was
wave propagating over a flat tank bottom with no breakwater models and then running up over
the beach. After this case was completed, we run experiments on waves propagating over various
submerged breakwater models including the plastic rectangular models, the foam rectangular
models, saw-tooth shaped angle models and the periodic semi-circular bump models. In this
chapter, we present the results from all the experimental cases, displaying them in tables in the
following sections. The results are for wave inundation and run-up against different initial wave
amplitude measured by the wave gauge WG1. Each case was ran once. All the results have been
non-dimensionalized by the still water depth which was 3 5/16 in in all the cases in this study.
4.1 Reference Case
The results of the reference case are shown in Table 4.1-1 and 4.1-2. These are the
results of run-up with no submerged breakwater model in the flume. The measurements are
divided by the water depth of 3 and 5/16 inches (or 8.4 cm).
34
Table 4.1-1: Reference case, 5 degree beach slope
5 degree reference
Amplitude Inundation Run-Up
0.032 0.524 0.046
0.063 1.155 0.101
0.075 1.583 0.138
0.117 1.810 0.158
0.127 2.179 0.190
0.148 2.869 0.250
0.174 3.667 0.320
0.207 4.167 0.363
0.233 4.643 0.405
0.258 5.286 0.461
Table 4.1-2: Reference case, 10 degree beach slope
10 degree reference
Amplitude Inundation Run-Up
0.018 0.357 0.062
0.049 0.690 0.120
0.079 1.048 0.182
0.107 1.655 0.287
0.112 1.714 0.298
0.139 2.321 0.403
0.169 2.667 0.463
0.198 3.071 0.533
0.244 3.655 0.635
0.258 3.750 0.651
35
4.2 Plastic Rectangular Model
The results of the plastic rectangular model with 5 degree beach slope at model lengths
2.5 ft, 5 ft, 7.5 ft, and 10 ft are shown below.
Table 4.2-1: Plastic Rectangular Model, L = 2.5 ft, 5 degree slope
Plastic Rectangle 2.5 ft 5 degrees Amplitude Inundation Run-Up
0.018 0.417 0.036 0.055 0.833 0.073 0.088 1.321 0.115 0.105 1.786 0.156 0.124 2.202 0.192 0.137 2.786 0.243 0.175 3.500 0.305 0.207 4.226 0.368 0.218 4.583 0.399 0.250 5.179 0.451
Table 4.2-2: Plastic Rectangular Model, L = 5 ft, 5 degree slope
Plastic Rectangle 5 ft 5 degree Amplitude Inundation Run-Up
0.019 0.298 0.026 0.057 0.690 0.060 0.077 1.405 0.122 0.107 1.714 0.149 0.121 2.024 0.176 0.132 2.440 0.213 0.162 3.036 0.265 0.188 3.571 0.311 0.210 3.929 0.342 0.245 4.643 0.405
36
Table 4.2-3: Plastic Rectangular Model, L = 7.5 ft, 5 degree slope
Plastic Rectangle 7.5 ft 5 degree
Amplitude Inundation Run-Up
0.020 0.333 0.029
0.063 0.905 0.079
0.071 1.333 0.116
0.110 1.714 0.149
0.123 2.190 0.191
0.139 2.702 0.236
0.164 3.071 0.268
0.208 3.976 0.347
0.229 4.393 0.383
0.257 4.726 0.412
Table 4.2-4: Plastic Rectangular Model, L = 10 ft, 5 degree slope
Plastic Rectangle 10 ft 5 degree
Amplitude Inundation Run-Up
0.040 0.357 0.031
0.048 0.631 0.055
0.083 1.286 0.112
0.119 1.845 0.161
0.126 2.036 0.177
0.143 2.917 0.254
0.175 3.369 0.294
0.200 3.655 0.319
0.230 4.690 0.409
0.257 4.857 0.423
37
The results of the plastic rectangular model with 10 degree beach slope at model lengths
2.5 ft, 5 ft, 7.5 ft, and 10 ft are shown below.
Table 4.2-5: Plastic Rectangular Model, L = 2.5 ft, 10 degree slope
Plastic Rectangle 2.5 ft 10 degrees
Amplitude Inundation Run-Up
0.021 0.286 0.050
0.061 0.976 0.170
0.073 1.238 0.215
0.108 1.286 0.223
0.140 1.595 0.277
0.175 2.060 0.358
0.182 3.060 0.531
0.190 3.238 0.562
0.219 3.536 0.614
0.271 3.893 0.676
Table 4.2-6: Plastic Rectangular Model, L = 5 ft, 10 degree slope
Plastic Rectangle 5 ft 10 degree
Amplitude Inundation Run-Up
0.018 0.405 0.070
0.048 0.869 0.151
0.071 1.012 0.176
0.106 1.417 0.246
0.123 1.786 0.310
0.146 2.024 0.351
0.165 2.500 0.434
0.194 3.310 0.575
0.224 3.548 0.616
0.257 3.750 0.651
38
Table 4.2-7: Plastic Rectangular Model, L = 7.5 ft, 10 degree slope
Plastic Rectangle 7.5 ft 10 degree
Amplitude Inundation Run-Up
0.019 0.381 0.066
0.052 0.726 0.126
0.104 1.107 0.192
0.119 1.429 0.248
0.152 1.750 0.304
0.157 2.083 0.362
0.171 2.536 0.440
0.202 2.988 0.519
0.223 3.298 0.573
0.250 3.571 0.620
Table 4.2-8: Plastic Rectangular Model, L = 10 ft, 10 degree slope
Plastic Rectangle 10 ft 10 degree
Amplitude Inundation Run-Up
0.019 0.667 0.116
0.062 1.238 0.215
0.069 1.357 0.236
0.090 1.429 0.248
0.125 1.643 0.285
0.162 2.083 0.362
0.185 2.500 0.434
0.187 2.560 0.444
0.226 2.988 0.519
0.268 3.405 0.591
39
4.3 Rectangular Foam Model
The results of the rectangular foam model with 5 degree beach slope at model lengths 2.5
ft, 5 ft, 7.5 ft, and 10 ft are shown below.
Table 4.3-1: Rectangular Foam Model, L = 2.5 ft, 5 degree slope
Foam Rectangle 2.5 ft 5 degrees Amplitude Inundation Run-Up
0.052 0.464 0.040 0.088 0.845 0.074 0.130 1.369 0.119 0.151 1.750 0.153 0.176 2.190 0.191 0.202 2.536 0.221 0.229 3.012 0.263 0.244 3.440 0.300 0.248 3.988 0.348 0.264 4.631 0.404
Table 4.3-2: Rectangular Foam Model, L = 5 ft, 5 degree slope
Foam Rectangle 5 ft 5 degree Amplitude Inundation Run-Up
0.052 0.393 0.034 0.085 0.940 0.082 0.118 1.167 0.102 0.152 1.679 0.146 0.181 2.226 0.194 0.212 2.560 0.223 0.236 2.976 0.259 0.245 3.476 0.303 0.249 3.905 0.340 0.282 4.464 0.389
40
Table 4.3-3: Rectangular Foam Model, L = 7.5 ft, 5 degree slope
Foam Rectangle 7.5 ft 5 degree
Amplitude Inundation Run-Up
0.061 0.417 0.036
0.089 0.917 0.080
0.124 1.524 0.133
0.152 1.917 0.167
0.170 2.190 0.191
0.198 2.405 0.210
0.217 3.071 0.268
0.230 3.274 0.285
0.242 3.750 0.327
0.277 4.631 0.404
Table 4.3-4: Rectangular Foam Model, L = 10 ft, 5 degree slope
Foam Rectangle 10 ft 5 degree
Amplitude Inundation Run-Up
0.057 0.583 0.051
0.081 0.964 0.084
0.106 1.357 0.118
0.131 1.810 0.158
0.163 2.071 0.181
0.199 2.679 0.233
0.219 3.095 0.270
0.230 3.286 0.286
0.251 3.786 0.330
0.271 4.048 0.353
41
The results of the rectangular foam model with 10 degree beach slope at model lengths
2.5 ft, 5 ft, 7.5 ft, and 10 ft are shown below.
Table 4.3-5: Rectangular Foam Model, L = 2.5 ft, 10 degree slope
Foam Rectangle 2.5 ft 10 degrees Amplitude Inundation Run-Up
0.019 0.179 0.031 0.074 0.476 0.083 0.102 0.798 0.139 0.119 1.107 0.192 0.167 1.512 0.263 0.196 1.940 0.337 0.206 2.214 0.385 0.226 2.536 0.440 0.255 2.750 0.478 0.281 3.119 0.542
Table 4.3-6: Rectangular Foam Model, L = 5 ft, 10 degree slope
Foam Rectangle 5 ft 10 degree Amplitude Inundation Run-Up
0.020 0.286 0.050 0.081 0.548 0.095 0.130 0.917 0.159 0.144 1.107 0.192 0.155 1.429 0.248 0.192 1.833 0.318 0.205 2.202 0.382 0.223 2.440 0.424 0.257 2.821 0.490 0.275 3.071 0.533
42
Table 4.3-7: Rectangular Foam Model, L = 7.5 ft, 10 degree slope
Foam Rectangle 7.5 ft 10 degree
Amplitude Inundation Run-Up
0.044 0.274 0.048
0.092 0.595 0.103
0.117 0.881 0.153
0.137 1.107 0.192
0.174 1.536 0.267
0.167 1.702 0.296
0.195 2.024 0.351
0.218 2.202 0.382
0.255 2.667 0.463
0.274 2.798 0.486
Table 4.3-8: Rectangular Foam Model, L = 10 ft, 10 degree slope
Foam Rectangle 10 ft 10 degree
Amplitude Inundation Run-Up
0.045 0.310 0.054
0.092 0.571 0.099
0.108 0.786 0.136
0.132 1.048 0.182
0.167 1.321 0.229
0.200 1.810 0.314
0.213 2.083 0.362
0.213 2.238 0.389
0.248 2.607 0.453
0.263 2.643 0.459
43
4.4 PVC Saw-Tooth Shaped Angle Model
The results of the PVC angle model with 5 degree beach slope at model lengths L1 =
19.7 in and L2 = 39.4 in are shown below.
Table 4.4-1: PVC Angle Model, L1, 5 degree slope
Angle L1 5 degree Amplitude Inundation Run-Up
0.019 0.464 0.040 0.049 0.786 0.068 0.071 1.083 0.094 0.119 1.524 0.133 0.125 1.821 0.159 0.160 2.107 0.184 0.183 2.548 0.222 0.210 2.964 0.258 0.243 3.500 0.305 0.274 3.679 0.321
Table 4.4-2: PVC Angle Model, L2, 5 degree slope
Angle L2 5 degree Amplitude Inundation Run-Up
0.019 0.214 0.019 0.064 0.583 0.051 0.101 0.810 0.071 0.121 1.107 0.096 0.131 1.452 0.127 0.155 1.714 0.149 0.188 2.036 0.177 0.211 2.333 0.203 0.238 2.607 0.227
44
The results of the PVC Angle model with 10 degree beach slope at model lengths L1 =
19.7 in and L2 = 39.4 in are shown below.
Table 4.4-3: PVC Angle Model, L1, 10 degree slope
Angle L1 10 degree Amplitude Inundation Run-Up
0.020 0.286 0.050 0.083 0.512 0.089 0.113 0.714 0.124 0.130 1.024 0.178 0.149 1.262 0.219 0.179 1.690 0.294 0.186 1.881 0.327 0.208 2.167 0.376 0.243 2.464 0.428 0.263 2.750 0.478
Table 4.4-4: PVC Angle Model, L2, 10 degree slope
Angle L2 10 degree Amplitude Inundation Run-Up
0.020 0.155 0.027 0.080 0.357 0.062 0.113 0.571 0.099 0.133 0.798 0.139 0.136 1.024 0.178 0.177 1.238 0.215 0.180 1.500 0.260 0.208 2.000 0.347 0.245 1.917 0.333 0.274 2.214 0.385
45
4.5 PVC Semi-Circular Continuous Bump Model
The results of the PVC semi-circular bump model with 5 degree beach slope at lengths
L3= 18.5 in and L4= 37 in are shown below.
Table 4.5-1: PVC Circular Model, L3, 5 degree slope
Circular L3 5 degree Amplitude Inundation Run-Up
0.020 0.369 0.032 0.086 0.726 0.063 0.106 1.071 0.093 0.133 1.607 0.140 0.155 1.905 0.166 0.175 2.310 0.201 0.190 2.857 0.249 0.208 3.179 0.277 0.240 3.750 0.327 0.268 4.548 0.396
Table 4.5-2: PVC Circular Model, L4, 5 degree slope
Circular L4 5 degree Amplitude Inundation Run-Up
0.020 0.262 0.023 0.077 0.726 0.063 0.085 1.095 0.095 0.131 1.429 0.125 0.126 1.881 0.164 0.155 2.321 0.202 0.180 2.667 0.232 0.205 3.226 0.281 0.239 3.536 0.308 0.271 4.083 0.356
46
The results of the PVC Circular model with 10 degree beach slope at lengths L3= 18.5 in
and L4= 37 in are shown below.
Table 4.5-3: PVC Circular Model, L3, 10 degree slope
Circular L3 10 degree Amplitude Inundation Run-Up
0.019 0.333 0.058 0.060 0.643 0.112 0.100 1.071 0.186 0.113 1.333 0.232 0.121 1.464 0.254 0.148 1.845 0.320 0.182 2.321 0.403 0.207 2.560 0.444 0.233 2.917 0.506 0.271 3.310 0.575
Table 4.5-4: PVC Circular Model, L4, 10 degree slope
Circular L4 10 degree Amplitude Inundation Run-Up
0.021 0.250 0.043 0.069 0.595 0.103 0.110 0.976 0.170 0.123 1.262 0.219 0.157 1.619 0.281 0.144 1.798 0.312 0.173 2.083 0.362 0.205 2.524 0.438 0.235 2.857 0.496 0.257 3.036 0.527
47
CHAPTER 5 ANALYSIS AND DISCUSSION
In this chapter, the experimental data are analyzed and discussed. We are especially
interested in comparing the effect of different types of submerged breakwater models in reducing
long wave run-up. The experimental data are also compared with Mohandie’s (2008) numerical
results regarding the optimal breakwater length in run-up reduction.
5.1 Rectangular Model Comparison, Foam Vs Plastic
The experiment was conducted twice – once with beach slope of 5 degree and again with
a beach slope of 10 degree. The analysis of the 5 degree beach slope will be reviewed first,
followed by the 10 degree beach slope analysis.
5.1-1 Run-up vs. wave amplitude on beach with 5 degree slope
The graph in Figure 5.1-1-1 compares the run-up in the case of the plastic rectangular
models of length of 2.5, 5, 7.5, and 10 ft., with that in the reference case. Figure 5.1-1-2
compares the run-up results in the case of the foam rectangular models of length of 2.5, 5, 7.5,
and 10 ft., with that in the reference case.
48
Figure 5.1-1-1: Run-up of a solitary wave on 5 degree beach after propagating over a plastic rectangular breakwater model.
Figure 5.1-1-2: Run-up of a solitary wave on 5 degree beach after propagating over a foam rectangular breakwater model.
49
A linear best fit trend line was created. Except for the case with L=2.5 ft for the plastic
model, the run-up for all other models are marginally reduced as compared to the reference case.
The foam model shows a significant effect in decreasing run-up compared with the plastic model.
Moreover, increasing the length of the breakwater only offers slight improvements for both
models – economically, it would make more sense to build the shorter model. Figure 5.1-1-3
shows the comparison of the run-up results between the cases of the plastic vs. foam model of 5
ft. length. Figure 5.1-1-4 shows the comparison of the plastic vs. foam model of 10 ft. length.
Figure 5.1-1-3: Plastic vs. Foam Run-up at 5 degree, L=5 ft
50
Figure 5.1-1-4: Plastic vs. Foam Run-up at 5 degree, L =10 ft
In both cases, the plastic breakwater model results in only minor run-up reduction
whereas the foam model results in more significant reduction.
5.1-2 Effect of model length on run-up reduction for 5 degree beach
The three graphs below show the comparison of the plastic vs. the foam model at specific
amplitudes for the effect of model length on run-up reduction. For the below comparisons, note
that the amplitude for each model is slightly different, since the wave maker cannot create the
exact same wave each time. However, the difference in amplitude is small and should not affect
the results significantly. To compare run-up reduction, a linear best fit line was created for the
reference case. The run-up in the cases with the breakwater models is then compared to the best
fit line at the same amplitude in the reference case to find the run-up reduction percent. The best
51
fit line for the reference case is R = 1.8368α - 0.0205 (r2 = 0.9835), where R is the run-up and α
is the amplitude of the initial wave.
Figure 5.1-2-1: Plot of run-up reduction vs. the ratio of breakwater model length over wavelength for α around 0.17; green triangles: plastic rectangular model, red squares:
foam rectangular model
52
Figure 5.1-2-2: Plot of run-up reduction vs. the ratio of breakwater model length over wavelength for α around 0.22; green triangles: plastic rectangular model, red squares:
foam rectangular model
Figure 5.1-2-3: Plot of run-up reduction vs. the ratio of breakwater model length over wavelength for α around 0.25; green triangles: plastic rectangular model, red squares:
foam rectangular model
53
For all four comparisons, the foam model consistently resulted in better run-up reduction
than the plastic model. The run-up between the foam models of different lengths is similar in all
four amplitude ranges whereas the plastic model varies. The plastic model also seems to have
the same trend across the different amplitudes. In the plastic models, the best model lengths are
in-between one to two times the wavelength. The result thus far has shown that the longer
breakwater model does not necessarily perform the best. The optimal breakwater length will be
further discussed in Section 5.4.
5.1-3 Run-up vs. wave amplitude on beach with 10 degree slope
The graph in Figure 5.1-3-1 below compares the run-up in the case of the plastic
rectangular model of length of 2.5, 5, 7.5, and 10 ft, with that in the reference case. Figure 5.1-3-
2 compares the run-up results in the case of the foam rectangular models of length of 2.5, 5, 7.5,
and 10 ft., with that in the reference case.
Figure 5.1-3-1: Run-up of a solitary wave on 10 degree beach after propagating over a plastic rectangular breakwater model.
54
Figure 5.1-3-2: Run-up of a solitary wave on 10 degree beach after propagating over a foam rectangular breakwater model.
For the 10-degree beach slope, the plastic models seem to perform worst. However, just
as the case with the 5 degree beach slope, the foam model consistently performs better than the
plastic model. Figure 5.1-3-3 shows the comparison of the plastic vs. foam model of 5 ft. length.
Figure 5.1-3-4 shows the comparison of the plastic vs. foam model of 10 ft. length.
55
Figure 5.1-3-3: Plastic vs. Foam Run-up at 10 degree, 5 ft L
Figure 5.1-3-4: Plastic vs. Foam Run-up at 5 degree, 10 ft L
56
For the 10 degree beach slope, the plastic model did not show any improvement. The
foam model still consistently performs better.
5.1-4 Effect of model length on run-up reduction for 10 degree beach
The three graphs below show the comparison of the plastic vs. the foam model at specific
amplitudes for the effect of model length on run-up reduction. Eqn. 2.7 was used to find the
wavelength of the generated wave. The model length was then normalized by water depth, ho of
3 5/16 inches and then divided by the calculated wave length. To compare run-up reduction, a
linear best fit line was created for the reference case. The run-up in the cases with the
breakwater models is then compared to the best fit line at the same amplitude in the reference
case to find the run-up reduction percent. The best fit line for the reference case is R = 2.5858α
+ 0.0085 (r2 = 0.991), where R is the run-up and α is the amplitude of the wave.
Figure 5.1-4-1: Plot of run-up reduction vs. the ratio of breakwater model length over wavelength for α around 0.11; green triangles: plastic rectangular model, red squares:
foam rectangular model
57
Figure 5.1-4-2: Plot of run-up reduction vs. the ratio of breakwater model length over wavelength for α around 0.14; green triangles: plastic rectangular model, red squares:
foam rectangular model
Figure 5.1-4-3: Plot of run-up reduction vs. the ratio of breakwater model length over wavelength for α around 0.26; green triangles: plastic rectangular model, red squares:
foam rectangular model
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For all three comparisons, the foam model consistently resulted in better run-up reduction
than the plastic model. It is clear that for the 10 degree beach test, the plastic models no longer
show a consistent trend.
Additional experiments were performed for waves of smaller amplitude over the plastic
rectangular models over the 10 degree beach by Mohandie. These results are shown in Figure
5.1.-4-4.
These results follow a similar trend to the results in the case with the 5 degree beach
slope, namely, there exists an optimal breakwater length with which the run-up reduction is the
maximum. However, it should be noted that for α = 0.062, the run-up reduction is unusually
high for a plastic rectangular model.
Figure 5.1-4-4: Model length vs. run-up reduction for 10 degree beach – smaller amplitudes
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5.2 PVC Model Comparison: Angle vs Semi-Circular
The experiment was conducted twice – once with beach slope of 5 degree and again with
a beach slope of 10 degree. The water depth in the experiments was h = 3 5/16 in. The height of
the angle model was d = 1.77 in or d/h = 0.53. For the semi-circular model, the model height d =
1.26 in, or d/h = 0.38. Two model lengths were tested in each case: L1 = 18.5 in and L2 = 37 in
for the semi-circular model, and L3 = 19.7 in and L4 = 39.4 in for the angle model. The
experimental results of run-up vs. initial wave amplitude are shown below.
Figure 5.2-1: Comparison of PVC models: Circular vs. Angle on 10 degree beach
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The Angle model performed better in both cases. More specifically, the semi-circular
model with length 18.5 inches performed the worst. The same model with twice the length
performed slightly better. The Angle model performed better than both semi-circular models –
with the longer Angle model doing even better. This increase in run-up reduction cannot be
solely attributed to the geometry, since the Angle models are higher. The detailed run-up
reduction is shown in the Table 5.2-1 and Table 5.2-2:
Figure 5.2-2: Comparison of PVC models: Circular vs. Angle on 10 degree beach
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Table 5.2-1:Run-up Reduction for all four PVC model setup 5 degree
Run-up Reduction Summary 5 degree Amplitude
Range Circular Angle
L1 L2 L3 L4
0.019 - 0.020 0.0% 0.0% 0.0% 0.0% 0.049 - 0.086 53.8% 48.0% 1.0% 47.9% 0.071 - 0.106 46.4% 29.2% 14.7% 57.3% 0.119 - 0.133 37.6% 43.4% 33.0% 52.4% 0.125 - 0.155 37.1% 22.4% 24.1% 42.5% 0.155 - 0.175 33.1% 23.3% 32.6% 43.4% 0.180 - 0.190 24.4% 25.0% 29.8% 45.4% 0.205 - 0.211 23.5% 20.9% 29.1% 44.5% 0.238 - 0.243 22.4% 26.5% 28.3% 45.5% 0.268 - 0.274 15.9% 25.6% 33.5% 46.0%
Table 5.2-2: Run-up Reduction for all four PVC model setup 10 degree
Run-up Reduction Summary 10 degree Amplitude
Range Circular Angle
L1 L2 L3 L4
0.019 - 0.021 0.0% 32.1% 18.4% 55.8% 0.060 - 0.083 31.3% 44.7% 60.3% 71.1% 0.100 - 0.113 30.3% 41.9% 58.8% 67.0% 0.113 - 0.133 23.1% 32.7% 48.3% 60.8% 0.121 - 0.157 21.2% 32.2% 44.3% 50.5% 0.148 - 0.179 17.9% 18.1% 37.6% 54.0% 0.173 - 0.186 15.9% 20.5% 33.2% 45.0% 0.205 - 0.208 18.3% 18.5% 31.2% 36.5% 0.235 - 0.245 17.2% 19.3% 32.8% 48.2% 0.257 - 0.274 19.1% 21.7% 30.7% 46.3%
Based on past results, it is expected that the longer the model the better (in this case)
since the longest model (L2 and L4 about 40 in) for both the semi-circular and Angle model are
less than one wavelength. Moreover, it is important to note that the dimensions of the Circular
model and the Angle model are different. The Angle model is taller and slightly longer. Since
the model lengths are about the same (37 in or 94 cm to 39.4 in or 100 cm), only the height will
be factored in the analysis. The figure below shows the run-up reduction of the models
normalized by model height. It should be noted that the model height might not correlate with
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run-up reduction proportionally. However, this is a better comparison than comparing just the
raw results.
Figure 5.2-3: PVC Model, Run-up Reduction Normalized by Model Height 5 degree
Figure 5.2-4: PVC Model, Run-up Reduction Normalized by Model Height 10 degree
63
Generally, Angle L4 has the highest run-up reduction in both 10 and 5 degree. The other
three configurations are similar in terms of run-up reduction. In the 10 degree beach slope, the
downward trend of run-up reduction is clearer. In this setup (10 degree beach), the Angle L3 and
semi-circular L4 offers similar run-up reduction, while the semi-circular L1 having slightly less
run-up reduction.
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5.3 PVC model vs. Rectangular Models
In this section, the results of the PVC models were compared with the rectangular models
to determine the significances of geometry of the breakwater in run-up reduction. However, the
d/h ratio for the PVC models and the rectangular models are not the same. The angular PVC
model has a d/h of 0.54 and the circular PVC model has a d/h of 0.38 while the rectangular
model has a d/h of 0.30. From previous sections, it is clear that the PVC model performed better
than the rectangular models – however, whether this is due to the geometry is unknown since the
d/h of both PVC models is bigger than the rectangular models. To test the claim that the
geometric factor played a significant role in run-up reduction, experimental data from
Mohandie’s work was used. Figure 5.3-1 shows the run-up on a 5 degree beach slope with a
rectangular breakwater of d/h = 0.65 and L/h of 14.6 (close to one wavelength). Both the d/h and
the length of the rectangular model are bigger than the PVC models (while length of model is
still less than one wavelength). (R/h w/reef is the rectangular breakwater case, and R/h w/o reef
is the reference case.)
65
For comparison, the graph with the same scale was created for the PVC models. As
shown below, the run-ups are lower in the PVC models as compared to the rectangular model.
For the rectangular case, run-up soar above 0.2 with wave amplitudes between 0.05 and 0.1,
whereas for the PVC models, run-up does not reach above 0.2 until pass wave amplitude of 0.15.
At the higher end, for the rectangular model, the run-up is about 0.35-0.4 at amplitude slightly
below 0.2, whereas for the PVC model, run-up remained below 0.35 when amplitudes are close
to 0.2. Note that the rectangular model should have performed better with a higher d/h. This
means that the geometric factor in the PVC models significantly reduced run-up even with lower
d/h (and the length).
Figure 5.3-1:Experimental Results from Mohandie (2007); Rectangular Rigid model 5 degree slope; d/h of 0.65
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Figure 5.3-2: Experimental results PVC model run-up; 5 degree slope
67
5.4 Experimental Plastic Rectangular Model vs. Mohandie’s (2008) Numerical Results
Regarding Optimal Breakwater Length
In this section, Mohandie’s (2008) 5 degree beach slope numerical data was compared
with the experimental results obtained in this study. Figure 5.3-1 below shows the theoretical
results compared to the experimental results. The red and blue lines near top of the graph are
numerical results compared to the experiment results in teal, green and purple.
The magnitude of the reduction in the experiments is somehow smaller. The
experimental data resulted in a run-up reduction of 0-10%, whereas the numerical has a run-up
reduction of 15-35%. The trend of the two are similar in that they both increase in run-up
reduction and then reduce as the model length increases. The optimal point for the numerical
simulation is about 2 times the wavelength whereas the experimental data varied. The table
below details the estimation of the optimal run-up reduction model length by interpolation.
Figure 5.4-1: Numerical vs. Experimental Results Plastic Rectangular Models
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Table 5.4-1: Optimal Model Length based on Rectangular Plastic Models
Amplitude Range Model length (in terms of wavelengths)
0.16-0.18 1.30
0.20-0.23 1.25
0.24-0.26 1.91
At the higher amplitude range, the experimental data quantitatively resembles the
numerical trend. The data also agrees with the numerical results that the longer model lengths
are not always better. Although this trend is not as clear in the Foam models. The figure below
shows the numerical results compared to the experimental results. We should point out that the
numerical results were obtained for impermeable rectangular breakwater models, not foam
porous models.
Figure 5.4-2: Numerical vs. Experimental Results Foam Model
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The downward trend of run-up reduction as model length increase is not as clear.
However, with exception of the last data point in the amplitude of 0.24-0.26 range, the run-up
reduction is generally decreasing as the model length increases pass 2 times the wavelength.
Moreover, the numerical results are based on a rigid rectangular breakwater. This trend might
not apply to flexible breakwaters such as the foam model. The numerical results were only for a
5 degree beach slope and the 10 degree data was not compared.
Lastly, the run-up reduction tables for the PVC models are repeated here below. For
these models, the model length is all under one wavelength. Hence, the longer model (L2 and L4)
should have a better run-up reduction, since it did not reach the optimal point yet. Out of the 38
comparisons (non-zero) 34 of the 38 have a better run-up when the model is twice the length.
Table 5.4-2: Run-up Reduction for PVC Models (Highlighted means higher reduction for 2L model) 5 deg
Run-up Reduction Summary 5 degree
Amplitude Range Circular Angle
L1 L2 L3 L4
0.019 - 0.020 0.0% 0.0% 0.0% 0.0% 0.049 - 0.086 53.8% 48.0% 1.0% 47.9% 0.071 - 0.106 46.4% 29.2% 14.7% 57.3% 0.119 - 0.133 37.6% 43.4% 33.0% 52.4% 0.125 - 0.155 37.1% 22.4% 24.1% 42.5% 0.155 - 0.175 33.1% 23.3% 32.6% 43.4% 0.180 - 0.190 24.4% 25.0% 29.8% 45.4% 0.205 - 0.211 23.5% 20.9% 29.1% 44.5% 0.238 - 0.243 22.4% 26.5% 28.3% 45.5% 0.268 - 0.274 15.9% 25.6% 33.5% 46.0%
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Table 5.4-3 Run-up Reduction for PVC Models
(Highlighted means higher reduction for 2L model) 10 deg
Run-up Reduction Summary 10 degree
Amplitude Range Circular Angle
L1 L2 L3 L4
0.019 - 0.021 0.0% 32.1% 18.4% 55.8% 0.060 - 0.083 31.3% 44.7% 60.3% 71.1% 0.100 - 0.113 30.3% 41.9% 58.8% 67.0% 0.113 - 0.133 23.1% 32.7% 48.3% 60.8% 0.121 - 0.157 21.2% 32.2% 44.3% 50.5% 0.148 - 0.179 17.9% 18.1% 37.6% 54.0% 0.173 - 0.186 15.9% 20.5% 33.2% 45.0% 0.205 - 0.208 18.3% 18.5% 31.2% 36.5% 0.235 - 0.245 17.2% 19.3% 32.8% 48.2% 0.257 - 0.274 19.1% 21.7% 30.7% 46.3%
5.5 Rectangular Models 5 ft Breakwater Spacing Configuration
This section details the brief study of using the breakwater models with a spacing in
between. The purpose of this is to see if a better breakwater configuration can be found by using
the same amount of materials. In this study, the 5 feet rectangular models were compared to two
2.5 feet rectangular models with a 5 feet spacing in-between the two breakwaters as shown in the
figure below.
R
60”
β
x
WG1 WG2
α
h0
wavemaker
Figure 5.5-1: Normal Experimental Setup with 5 ft model used for comparison
1”
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Table 5.5-1 to Table 5.5-4 below show the results for the test runs for the foam and
plastic rectangular models at 5 and 10 degree beach slope. The measurements and run-up are
normalized by the water depth.
Table 5.5-1: Plastic Rectangle 5 ft with spacing (5 ft) 5 degree
Plastic Rectangle 5 ft with spacing (5 ft) 5 degree Amp Raw Measurement Run-Up 0.020 0.381 0.033 0.071 0.821 0.072 0.083 1.262 0.110 0.112 1.631 0.142 0.124 2.321 0.202 0.152 2.417 0.211 0.168 3.024 0.264 0.198 3.738 0.326 0.227 4.238 0.369 0.254 5.000 0.436
R
β
x
WG1 WG2
α
h0
wavemaker
Figure 5.5-2: Experimental Setup of breakwater model with spacing
1”
30” 30” 60”
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Table 5.5-2: Plastic Rectangle 5 ft with spacing (5 ft) 10 degree
Plastic Rectangle 5 ft with spacing (5 ft) 10 degree Amp Raw Measurement Run-Up 0.038 0.500 0.087 0.081 0.869 0.151 0.118 1.095 0.190 0.154 1.452 0.252 0.173 2.262 0.393 0.194 2.690 0.467 0.223 2.964 0.515 0.230 3.464 0.602 0.238 3.571 0.620 0.267 3.690 0.641
Table 5.5-3: Foam Rectangle 5 ft with spacing (5 ft) 5 degree
Foam Rectangle 5 ft with spacing (5 ft) 5 degree Amp Raw Measurement Run-Up 0.051 0.488 0.043 0.081 0.821 0.072 0.112 1.214 0.106 0.127 1.571 0.137 0.162 1.988 0.173 0.194 2.345 0.204 0.221 2.762 0.241 0.233 3.262 0.284 0.238 3.631 0.316 0.270 4.179 0.364
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Table 5.5-4: Foam Rectangle 5 ft with spacing (5 ft) 5 degree
Foam Rectangle 5 ft with spacing (5 ft) 10 degree Amp Raw Measurement Run-Up 0.032 0.274 0.048 0.040 0.524 0.091 0.067 0.893 0.155 0.089 1.155 0.201 0.131 1.440 0.250 0.160 1.714 0.298 0.167 2.167 0.376 0.207 2.381 0.413 0.237 2.643 0.459 0.256 2.917 0.506
Figure 5.5-3 to Figure 5.5-6 below compare the 5 feet breakwater models (in two 2.5
feet) with 5 feet spacing to their respective model and beach slope of the normal 5 feet
rectangular breakwater model.
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Figure 5.5-3: Plastic Model with spacing comparisons 5 degree
Figure 5.5-4: Foam Model with spacing comparison 5 degree
75
Figure 5.5-5: Plastic Model with spacing comparisons 10 degree
Figure 5.5-6: Plastic Model with spacing comparisons 10 degree
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In the 5 degree beach slope, there are no significant differences between the 5 ft. and the
5 ft. with spacing models. However, in the 10 degree beach slope, a slight difference can be seen
between the two models. Moreover, the plastic and foam models behaved differently. The
model with spacing performed better in the plastic model whereas the model with no spacing
performed better in the foam model. Upon closer look in the 5 degree beach slope test runs,
although the difference is small, the two models also follow the same trend – for plastic model,
the model with spacing performed better, and for foam model the model with no spacing
performed better.
5.6 Errors and Accuracies
Errors are bound to exist in experimental studies. In this study, there are many different
equipment working together and many different measurements that are needed to be made. The
accuracies of the wavemaker and the wave gauges are described in a previous section in Chapter
3. The water level, and inundation are manually measured with a ruler with millimeter accuracy.
The beach slope is measured by Johnson Magnetic Angle Locator with at accuracy of 1 degree.
It is important to note that there is possibility of human error, as each data point required the
input of a new wave file into the computer, a manual split second measurement of the wave
inundation, and the exporting of the wave amplitude from the computer. These are all possible
errors that, although were minimized by following procedure, should be acknowledged.
In addition to the possible errors listed above, friction due to fluid viscosity and the
narrow flume size walls and flume bottom was not accounted for in the present analysis nor in
the numerical results based on the inviscid wave theory.
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CHAPTER 6 Conclusion
6.1 Summary of work and findings
The following are the findings of this study:
• Experimental results found that the rectangular plastic model did not have a significant
impact on run-up reduction.
• Experimental results strongly support that foam/flexible and porous material are better
than plastic/rigid and impermeable material for submerged breakwaters.
o The rectangular plastic models have a run-up reduction of around 0-20%.
o The rectangular foam models have a run-up reduction of around 25-50%.
• Experimental results in this study also showed that the saw-tooth shaped breakwater
model has a better effect in reducing the wave run-up, however, since the model height of
d/h = 0.58 is higher than the other models, the added reduction could be partially due to
the geometry and partially due to the increase in model height. This issue needs further
research by maintaining the same model height d/h in all the experiments in order to
single out the effect of breakwater geometry on wave run-up reduction.
o Further analysis by comparing the PVC angular and circular models to
rectangular models with a higher d/h show that the PVC angular and circular
models still has a better run-up reduction. It can be concluded the geometric
factor played a role in the run-up reduction.
• Experimental results generally agree qualitatively with the numerical simulation done by
Mohandie and Teng (2012) that an optimal breakwater length exists for run-up reduction.
78
o The rectangular plastic models follow the same trend as the numerical results of
increasing run-up reduction to a certain point than decreasing as the model length
increases. However, the magnitudes of the reduction are significantly different.
o The numerical results seems that the optimal breakwater length is two times the
wavelength whereas, the experimental data ranged from 1.25-2.00 times the
wavelength.
o The magnitudes of the run-up reduction % between the numerical and
experimental data are off by about 20%. This represents a magnitude difference
of over 2 times.
o The rectangular foam model very slightly follows the trend of the numerical
results. The difference may be due to the fact that the numerical results are based
on a rigid rectangular breakwater.
o Out of the 38 (non-zero) comparisons between model lengths of L1 vs. L2 and L3
vs. L4 for the circular and angular models, 34 of the 38 points have a better run-up
reduction for the longer model. For all the PVC models, the model lengths are
less than one times the wavelength.
• Experimental results for breakwater configurations with spacing for 5 degree beach slope
show no significant difference when compared to a breakwater model with no spacing.
• Experimental results for breakwater configuration with spacing for 10 degree beach slope
showed mixed results between the plastic and foam models. The plastic model showed
better run-up reduction for the breakwater with spacing and the foam model showed
better run-up reduction for the breakwater without spacing.
79
Based on the observations above, a rigid rectangular breakwater with a smooth surface is
not recommended. Although, the numerical studies has shown a higher run-up reduction for
these models – more work needs to be done to investigate this matter. Despite the significant
magnitude differences between the numerical and experimental studies, both agree that an
optimal breakwater length exist. Compared to rectangular plastic (rigid) model, the
rectangular foam model offers a significantly higher run-up reduction. Although a foam type
material may never be practical, the importance is the finding that the flexible, porous, and
rough surface was responsible for the increased run-up reduction. Lastly, this experimental
study has shown that breakwater models with saw-tooth geometry are better than rectangular
breakwaters. However, the degree of additional run-up reduction is not clear due to the
physical dimensional differences of the models in this study. Section 6.2 highlights several
recommendations that can be done to further investigate several issues found in this study.
6.2 Recommendations
For future studies, I would recommend the following:
• To better compare against numerical results, I recommend testing a finer range of
model length. In this study, a single model was tested over 10 different
amplitudes, which was useful in seeing run-up reduction over a large range of
amplitudes. However, when comparing model lengths, the data was lacking. I
suggest focusing on a few amplitudes and a larger/finer range of model length.
• This study has shown that a foam type material is better than rigid models as well
as using other geometry is better than a plain rectangular model. It will be
interesting to see the results for non-rectangular foam models.
80
o Furthermore, the reason for the better run-up reduction from the foam
model is not clear. Since the breakwater model is flexible, porous, and has
a rough surface as compared to the plastic rectangular model. An
experimental study to isolate and test each factor of the foam model would
be interesting.
• For this study, it was difficult to compare all the models due to different
parameters. I recommend using similar dimensions, (length and d/h).
• To further standardize procedures and to better compare results among different
studies, I recommend marking and recording equipment/breakwater locations.
• Lastly, to mitigate error and for better comparison of results, I recommend
repeating the trials runs. This will reduce errors and increase confidence in the
results. This will also created a standard of error in order to judge whether or not
the findings are significant or due to chance.
81
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