Miami
Beach 32nd Street Hot Spot:
Numerical Modeling & Design
Optimization
ABSTRACT
The shoreline in the vicinity of 32nd street, Miami Beach
has been established as an erosional hot spot. A coastal processes
analysis performed by Coastal Systems International, (Coastal
Systems), determined that the highly localized levels of erosion
were due to the presence of a shoreline protrusion at the
hot spot. Numerical modeling of the 32nd Street area confirmed
that prevailing wave conditions could generate a strong gradient
in wave energy capable of causing localized erosion. This
earlier study recommended the use of three artificial headlands
to gradually transition the shoreline and to dissipate much
of the localized wave energy.
This paper presents the results of numerical two-dimensional
wave and current modeling that was conducted to etermine the
effect of the proposed artificial headlands on the existing
longshore currents. The results of the wave current modeling
coupled with the Parabolic Bay Theory (Hsu and Silvester,
1993) showed that the configuration of the structures could
be optimized to increase the stabilized area and mitigate
down-drift impacts.
INTRODUCTION
Erosional hot spots are areas within a littoral cell that
experience higher than average levels of erosion. Therefore,
the erosional activity at hot spots can govern the frequency
of beach re-nourishments for a stretch of shoreline. The mechanisms
for the localized levels of higher erosional activity, while
not fully defined, are speculated to include irregularities
in the shoreline, offshore bathymetry, coastal development,
etc. The study of the causes of hot spots can provide design
criteria to increase the performance of beach renourishment
projects. This hot spot countermeasure approach can provide
construction cost savings over the life of a project.
The Miami Beach littoral cell extends from Baker's Haulover
Inlet to Government Cut, a distance of approximately 3 miles.
The 32nd Street shoreline is part of The Beach Erosion and
Hurricane Protection Project for Dade County-a federally sponsored
project. A study of the Dade county regional sediment budget
(Coastal Systems, 1997) that considered the performance of
beach nourishments since the inception of the federal project
determined the existence of several hot spots within the county.
One of the more severely eroding areas within the county was
the 32nd Street area of Miami Beach, where the shoreline receded
an average of 17 feet per year (5.2 m/yr) from 1980 to 1996.
It was concluded that the higher localized levels of erosion
of the shoreline near 32nd Street were due to a protrusion
of the shoreline resulting from post-war development beyond
the historical dune line. Furthermore, it was concluded that
an overall change in the shoreline orientation near 32nd Street
could be partly responsible for the increased erosion rate.
A more detailed study of the 32nd Street hot spot (Coastal
Systems, 2000) examined possible stabilization alternatives
based on predicted performance, construction cost, and potential
downdrift and environmental impacts. The study used numerical
models including GENESIS and REF-DIF to predict shoreline
response to the various stabilization schemes. The results
of the REF-DIF modeling demonstrated that offshore bathymetry
coupled with the change in shoreline orientation did promote
the focusing of wave energy in the 32nd Street area. These
factors were predominantly responsible for the presence of
the hot spot. In addition, the study concluded that the protrusion
of the shoreline would potentially cause any unprotected beach
fill to be 'sheared off' rapidly. The use of structures to
'step' the change in shoreline orientation would result in
better beach fill performance. The study recommended the construction
of three artificial headlands coupled with beach fill as the
best alternative for meeting the project goals.
In this study, the possible impacts of headland construction
on the waves and currents were examined to determine the effects
of the structures on the existing longshore currents and the
corresponding littoral drift in the region. Two dimensional
numerical wave models were applied to offshore hindcast wave
data in order to predict the nearshore wave field. The results
of the wave model were used to simulate the longshore currents
at the site, both before and after the construction of the
artificial headlands. The current model demonstrated the headlands
did not block or significantly redirect longshore currents.
However, the testing of alternate configurations permitted
the optimization of the headland configuration, minimizing
the interference of the structures on the longshore drift,
while enhancing the protection at the hot spot.
Procedure
The MIKE 21 wave and hydrodynamic modeling package developed
by the Danish Hydraulic Institute (DHI) was used to simulate
waves and currents at the hot spot. Several components of
the MIKE 21 package were used. Beach, and the average hindcas
wave conditions are presented in Figure
2. The average wave condition was found to be a significant
wave height The Nearshore Spectral Wave (NSW) module was used
to simulate the transformation of offshore waves to the nearshore
region. The NSW model encompassed 7.2 miles by 7.8 miles,
centered on the hotspot including an alongshore resolution
of 250 feet (75 m). The results of the NSW model were transferred
to a more localized Parabolic Mild Slope (PMS) model, which
was better able to simulate wave refraction, diffraction and
breaking processes on a finer scale. Finally, the wave radiation
stress field derived from the PMS model was used to simulate
wave-driven currents with the Hydrodynamic (HD) model. The
modeled area for the PMS and HD models was 1.5 miles by 1.1
miles, centered on the hotspot, and an alongshore resolution
of 8 feet (2.5m) feet. The layout of both model areas relative
to the hot spot is shown in Figure 1.
Initially the entire procedure was performed for the present
conditions and then was repeated with the structures in place
to gauge the impact of the headlands.
Bathymetry
Nearshore bathymetric data was collected by a hydrographic
survey conducted in December 1999 by Coastal Systems. Offshore
bathymetry data from the June 1998 Morgan & Eklund survey
and National Oceanographic and Atmospheric Administration
(NOAA) bathymetric charts were used to supplement the Coastal
Systems' data for the NSW model.
Structures
The bathymetry data was adjusted within MIKE21 to incorporate
the artificial headlands and the pre-filled shoreline. Several
configurations of the structures were simulated, and two configurations
are presented herein: the original configuration as recommended
by the 1997 study and an optimized configuration. Both configurations
consist of three artificial headlands of approximate crest
lengths of 210, 180 and 75 feet and breadth at the mean water
line of 25 feet. The structures are arranged to step the shoreline
through its change in orientation. In the original configuration
the northern two structures had hooks to extend the diffraction
point further offshore and minimize downdrift impacts. The
optimization process determined that straightening the structures
by removing the hooks created a more favorable profile with
respect to the predominant longshore drift.
Wave Information
The wind and wave data for the analysis were obtained from
the U.S. Army Corps of Engineers through their Wave Information
Study (WIS) and Coastal Field Data Collection Program. This
data is based on the results of an 18 year (1976-1993) hindcast
that included the effects of hurricanes and tropical storms.
Data collected at WIS Station #8 was analyzed in order to
obtain representative conditions offshore of Miami of Hs=3.3
feet (1.0m), and average wave period of 5.4 seconds from the
Northeast. However, a wide range of periods are associated
with this wave height and direction, therefore simulations
were also performed for wave periods of 7.4, 9.4, and 11.4
seconds, respectively. Offshore waves were modeled by generating
irregular directional wave spectra, and applying this condition
along the offshore boundary. Directional rather than unidirectional
waves were used in this study to prevent
over-focusing of wave energy during the refraction calculations.
Wave Transformation Results
Present Conditions: Figure 3, shows
the results of the Parabolic Mild Slope wave model (Hmo=1.0
m, Tp=5.4 sec, NE) [note that north is oriented downward for
all figures]. Wave heights are shown by colored contours and
the wave direction is shown by the vectors. The refraction
of the waves is apparent from intermediate depths. The refraction
occurs gradually until very near the shoreline. The wave breaking
process is visible in the decay of wave height nearshore,
the breaking wave height was found to range from 2.3 to 3.0
feet (0.7 to 0.9 m). There is a longshore variation in the
breaking wave height because irregular bottom contours focus
and diffuse wave energy. Under this wave climate the breaker
line ranges from 200 to 250 feet (60 to 75 m) offshore. Note
that at the breaker zone the waves remain angled with respect
to the shoreline. This difference in wave direction is the
driving force for longshore currents. The results of the wave
model were validated with small amplitude wave theory. The
modeled shoaling, refraction and breaking processes compared
well with analytical theory.
Original Headland Configuration:
Figure 4 shows the wave field in
the presence of the hooked headlands (Hmo=1.0 m, Tp=5.4 sec,
NE). Note the shadow zone, in the lee of the headlands where
minimal wave energy is present. Refraction and diffraction
around the headlands can be observed in the direction of wave
propagation. Wave heights inside the bays are much smaller
than just offshore of the headlands as a result of the shelter
provided by the headlands.
Optimized Headland Configuration:
Figure 5 shows the wave field in
the presence of the artificial headlands. As in Figure
4, a shadow zone can be observed in
the lee of the headlands. However, in the latter case
the sheltered area is not as large due to the lack of hooks,
though the calculated wave heights inside the bays are not
significantly larger. This constancy of wave height is a result
of the height of broken waves being solely determined by water
depth.
Effect of Wave
Period: Compared with the shorter period waves, the
longer period waves experienced more refraction, and the waves
reached the shore in a more perpendicular manner. Additionally,
shoaling effects were increased and the waves achieved larger
breaking wave heights, to a maximum height of 3.8 feet (1.15
m). Consequently, the breakpoint was shifted offshore and
the surf zone was wider. The water depth governs the height
of the broken waves, thereby producing results inside the
bays that are very similar for waves of all periods.
Current Model Results
Present Conditions: The HydroDynamic
model results for the wave field in the absence of structures
is shown in Figure 6. Current direction
is represented by vectors and its speed by contours. The following
observations can be made: in the surf zone the longshore current
is strongest and is generally parallel to the shoreline; beyond
the breaker zone there is some return flow though current
speeds are much smaller. Surf zone current speeds reach a
maximum of 1.5 feet/sec (0.45 m/s).
Original Headland Configuration:
In Figure 7 the flow pattern near
the headlands is shown. The predominant southern longshore
current is redirected around the system of headlands. The
total flow past the site is maintained when compared with
the present conditions due to slower currents in deeper water.
The effect of the structures is realized as far as 400 feet
(125 m) north, as represented by the current pattern beginning
to veer away from shore at this location.
The gap between the headlands is small enough that the longshore
current bypasses each bay. This current pattern is advantageous
from the standpoint of the stability of the bays, as the longshore
current cannot erode the sand of the pocket beaches. Within
the bay, eddies are observed with maximum currents of 1.5
feet/sec (0.44 m/sec). Furthermore, there is a small exchange
of flow between the bay and the current at the seaward edge
of the bays. There are no rip currents apparent nor do the
currents near the headlands or inside the bays exceed those
observed in the absence of structures.
Downstream of the headlands the currents turn shoreward,
with the current pattern returning to the undisturbed condition
approximately 200 feet (60m) to the south. It is expected
that the point at which the flow regime returns to the undisturbed
conditions effectively represents the limit of potential downdrift
erosion.
Optimized Headland Configuration: The currents generated
by the wave field can be found in Figure
8. The results are similar to those observed in Figure
7, but they are less disrupted with respect to the present
condition. The simple headlands appear to present a less significant
obstacle to the longshore current than the hooked headlands.
When the current vector plots are compared, the streaming
of the current around the three simple headlands is less disrupted
than it is around the hooks. There is a greater extent of
redirection of the longshore flow offshore by the hook-which
could result in sediment being lost to the system. Secondly,
the eddies within the bays are smaller and the associated
currents of lesser magnitude (up to 1.0 feet/sec, 0.3m/s).
Effect of Wave Period: In general,
currents and flows associated with longer period waves were
of slightly higher magnitude-about 10% greater, though the
current patterns were identical. The increased energy at the
breakpoint, from the larger breaking wave heights, was offset
by the lower angle of attack. Thereby resulting in longshore
currents with approximately the same velocity for all periods.
CONCLUSIONS
The effect of the construction of three artificial headlands
was examined through numerical modeling techniques. The original
configuration proposed in an earlier study was optimized to
effectively streamline the structures with respect to the
predominant longshore currents. The structures were found
to have an impact on the shoreline approximately 400 feet
(120m) updrift and 200 feet (60m) downdrift. For the optimized
configuration, the flow patterns were not significantly diverted
or decelerated by the structures. The partial exchange of
water from within the crenulate bays and the longshore current
was observed.
The headland design was revisited in light of the findings
of the hydrodynamic modeling, recent site surveys, and past
coastal engineering research, specifically parabolic bay theory
(Hsu and Silvester, 1993). In any shore protection scheme,
two effects are certain: that up-coast of the structure sediment
will be impounded, and that down-coast there will be some
erosion. Thus, the most efficient design will maximize the
positive impact of the accretion while minimizing the negative
impact of the erosion.
Accretion of sand is needed most at the hot spot, not north
of the hotspot. The current modeling showed that the effect
of the structures was felt as far as 400 (120m) feet to the
north. Repositioning the system of headlands further south
would result in concentrating more accretion at the hot spot
rather than areas to the north.
Repositioning the system of headlands to the south would also
reduce the erosional impact down-coast of the headlands. The
optimized headland system terminates in an area of coast where
the beach is still marginal, and is transitioning from erosional
to relatively stable. Since some recession of the shoreline
is to be expected at the terminus, relocation to a wider,
less eroding beach area would mitigate potential impacts.
Finally, relocating the southernmost headland closer to shore
can reduce the amount of erosion at the terminus of the headlands.
This effectively reduces the size of the shadow-zone behind
the headland, and it is in this shadow-zone that erosion occurs.
The system of headlands would then be more streamlined and
longshore currents would more quickly transition back to the
undisturbed patterns.
Adam M. Shah P.E.-Project Manager, CSI
R. Harvey Sasso P.E.-Principal, CSI
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The 32nd Stret Breakwaters as the currently
stand. |
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Figure 3: Results of Wave Model-Present
Condition |
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Figure 4: Results of Wave Model-Proposed
Configuration |
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Figure 5 : Results of Wave
Model-Optimized Configuration |
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Figure 6 : Results of Current Model-Present
Condition |

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Figure 7 : Results of Current Model-Proposed
Configuration |
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Figure 8 : Results of Current Model-Optimized
Configuration |
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REFERENCES
Brooks, R.M. and Brandon, W.A. (1995). "Hindcast
Wave Information for the U.S. Atlantic Coast: Update
1976-1993 with Hurricanes," WIS Report 33, U.S.
Army Engineer Waterways Experiment Station, Vicksburg,
MS.
Coastal Systems International, "Dade County Regional
Sediment
Budget," Submitted to the Department of Environmental
Resources
Management, Dade County, Florida, 1997.
Coastal Systems International, "City of Miami Beach
Erosional Hot
Spots," Submitted to the Department of Environmental
Resources
Management, Dade County, Florida, 2000.
Hsu, J.R. and Silvester, R. (1993), "Coastal Stabilization-Innovative
Concepts," New Jersey: Prentice Hall.
Wiegel, Robert L., "Dade County, Florida, Beach
Nourishment and
Hurricane Surge Protection," Shore and Beach -
Journal of the American Beach Preservation Assoc., Volume
60: No. 4, October 1992 |
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