Conference PaperPDF Available

Review of existing multi-functional artificial reefs

Authors:
  • Griffith University; International Coastal Management

Abstract and Figures

Costs, benefits and performance of existing surfing and multi-functional artificial reefs have varied considerably. This paper compares details of the 6 reefs completed or under construction to determine the total costs and performance as well as construction issues. The investigation was undertaken as part of the design and construct contract for a multi-functional artificial reef project.
Content may be subject to copyright.
AUSTRALASIAN CONFERENCE ON COASTS AND PORTS 2007
1
Review of Existing Multi-Functional Artificial Reefs
Leslie (Angus) Jackson1 and Bobbie B Corbett1
1International Coastal Management, Queensland
Abstract
Costs, benefits and performance of existing surfing and multi-functional artificial reefs have varied considerably.
This paper compares details of the 6 reefs completed or under construction to determine the total costs and
performance as well as construction issues. The investigation was undertaken as part of the design and construct
contract for a multi-functional artificial reef project.
1 Introduction
Coastal engineers have been aware of the need to
include surfing into design of coastal structures and
there are numerous examples in Australia, and
worldwide, where coastal protection works have
improved surf amenity. Most artificial “surf” reefs to
date have been constructed in Australia. However, the
design of such structures is difficult as there is a lot of
conflicting information on the performance of the
existing reef projects.
Despite considerable interest in multi-functional
artificial reefs (MFAR), only 4 have been totally
completed to date, and a further 2 commenced:
Completed as at 1-3-07
Bargara, Queensland, Australia 1997
Cables, Western Australia, Australia 1998-99
Narrowneck, Queensland, Australia 1999-00
Pratte's Reef, El Segundo, USA 2000-01
Near Completed as at 1-3-07
Mount Maunganui, NZ 2005 - ??
Construction commenced as at 1-3-07
Opunake, NZ 2006 -???
Detailed technical monitoring reports have been
published on all of the completed reefs, except
Bargara. This published technical data, with
additional research and observations, has been used in
this review of the following reef characteristics:
Location and site conditions (waves and tides)
Design - size and shape
Construction materials and methods
Costs [total & $/m3]
Performance
Coastal protection / salient
Safety
Amenity created e.g. surfing, diving and
fishing
Comments and lessons learned
2 Bargara Reef
2.1 Location and site conditions
Bargara is located at the northern end of Hervey Bay
in Queensland. Waves are generally < 1 m. The most
common occurring swell is 0.2 – 0.4m with periods of
6 – 9 sec [BPA, 1986]. Tides are semi diurnal with a
spring tidal range of about 2.5m
2.2 Design
The site is on the north side of a headland and is
effectively a ½ V. The objective was to smooth the
existing bathymetry to give a break that was rideable
without abrupt interruptions [Pitt, 2005].
No modeling was carried out. Local knowledge was
used to relocate / break boulders that were observed to
be adversely impacting on the break. These boulders
were also used to fill holes to further improve the wave
quality for surfing. The initial works were monitored
on the “full scale model” and additional works have
been “designed” [Figure 1]. [Redgard, 2006]
Figure 1 Bargara Reef Phase 3 [Source: Greg Redgard]
2.3 Construction materials and methods
The rocky headland was groomed at low tide using a
large excavator to move the existing basalt boulders
(Figure 2). No additional materials were required to be
imported. The rock volume moved is very difficult to
estimate, but is approximately 300m3.
Figure 2 Excavator moving boulders at low tide
(Source: Greg Redgard)
AUSTRALASIAN CONFERENCE ON COASTS AND PORTS 2007
2.4 Cost
Costs incurred to date have been ~A$10,000, including
approvals, but not including considerable time
contributed by the community (Redgard, 2006). This
is equivalent to ~A$30/m3.
2.5 Performance
No scientific monitoring has been done. It is obvious,
however, that the work is producing an improved and
safer, longer point break [Figure 3] near high tide with
swells of over about 1m and light and / or offshore
winds. The number of surfable days is relatively low,
but expectations of the surf quality do not appear
unrealistic and it is seen as successful in improving the
surf quality and increasing the number of surfable
days. (Redgard, 2006)
There have been no reports found of any serious
injuries. The reef works would have had no significant
affect on coastal processes on the rocky headland.
Figure 3 Surf at Bargara (Source: Greg Redgard)
2.6 Comments
The following comments and conclusions can be
made:
The emphasis has been to “improve” local
conditions, not create a new surfing location. With
realistic expectations, the project is generally seen
as successful at a local level.
The reef only works at high tides.
The avoidance of expensive modeling and use of
community involvement, simple construction
methodology and local equipment has resulted in
a low total and unit cost.
The site is rough boulders, but there have been no
reports of injuries.
Monitoring would be very beneficial.
3 Cables Reef
3.1 Location and site conditions
Cables Reef is located at Perth, Western Australia.
Tide is diurnal with a spring tidal range of 0.4m.
Mean wave conditions are characterized by a
significant wave height (Hs) of 2.0m and a spectral
mean wave period (Tm) of 8.8s although there is
considerable seasonal variability (Lemme et al, 1999).
3.2 Design
Engineering for the final design and construction of
the project was coordinated by the WA Department of
Marine and Harbours. The Centre for Water Research
at the University of Western Australia assisted the
Department in the design aspects. A large number of
comprehensive studies were undertaken and the
outcomes have been published (Pattiaratchi, 1997).
The final reef shape (Figure 4) chosen was a
“Boomerang shaped” reef with a nose ½ angle of
approx. 45deg. Crest height was set at -1m LAT for
safety. To minimize volume, the reef was on a natural
nearshore rocky reef.
Figure 4 Cables Reef - initial shape and extension
(Source: tender documents, 1999)
3.3 Construction materials and methods
Detailed construction design was undertaken by the
WA Dept of Transport with project management by
Egis consulting. The reef was constructed with
5,500m3 of 1.5t and 3.0t stone. The contract was
awarded to WA Limestone with construction being
undertaken using a barge transporting the granite stone
material from Fremantle Harbour (Figure 5).
Figure 5 Excavator placing rock at Cables (Source:
Pattiaratchi, 2003)
3.4 Cost
The total cost was $1.8M (DPI, 1999). This is
equivalent to ~A$327/m3.
3.5 Performance
Monitoring of the reef has been carried out by
Bancroft [1999] and Pattiaratchi [2003]. They
concluded that the reef was performing according to
design, with swell as low as 0.5m breaking on the reef
in low tides. In 1999, the reef was considered to be
“surfable” 142 days of the 178 days it was breaking.
(Figure 6)
AUSTRALASIAN CONFERENCE ON COASTS AND PORTS 2007
Figure 6 Surf at Cables
3.6 Comments
The following comments and conclusions can be
made:
The location has abundant swells and a low tide
variation that are suitable for a surfing reef.
The project appears to have “improved” surfing
conditions when swell, tide and wind conditions
are suitable.
The reef does provide a quality surf wave at times,
but it has not gained a reputation as a great surf
spot. Part of the reason for this appears to be that:
There are a number of good surf breaks in the
area
When conditions favour the reef, a number of
other local breaks work as well
The reef takeoff area is about 300m offshore
[other natural breaks are closer to shore]
No reports of injuries have been noted.
4 Narrowneck Reef
4.1 Location and site conditions
Narrowneck Reef is located on the Gold Coast,
Queensland. It is part of the Northern Gold Coast
Beach Protection Strategy (Gold Coast City Council).
The site experiences high wave energy and a nett
northerly sand transport rate of ~500,000m3 pa.
Average Hs is about 1.0m but Hm has exceeded 12m
since construction. Tide is semi-diurnal with a spring
tidal range of 1.3m
4.2 Design
The primary function of the reef was coastal
protection, with “improved surfing” as a secondary
objective. The final design (Figure 7) was determined
by ICM based on the recommendations of the Uni of
Waikato , additional numerical and physical modeling
by WRL [Uni of NSW] and Griffith Uni and extensive
monitoring.
Figure 7 Narrowneck design; black = original
footprint, colours = design contours after monitoring
The reef is a flared V-shape with a nose ½ angle of
~13deg separated by a bridged central paddle channel.
Design crest height was reduced to -1m LAT [from
0.0m LAT recommended by Uni of Waikato] due to
concerns regarding safety – surfers and rips. The reef
volume is very large [approx. 70,000m3].
4.3 Construction materials and methodology
ICM developed the construction methodology and the
contract was awarded to local firm McQuade Marine.
The reef was constructed using over 400 mega sand-
filled geotextile containers supplied by ELCO
Solutions [then SoilFilters Australia], filled, and
dropped into place using a hopper dredge, Faucon
[Figure 8].
Figure 8 Placing containers from a split hull hopper
dredge at Narrowneck
The seabed at the inner section of the reef can vary by
up to 2m due to the migration of the storm bar. A very
large storm bar had formed over the back half of the
reef prior to construction and a sequenced construction
was undertaken with top-up after migration of the bar
shoreward [and resulting “settlement” of the reef].
4.4 Cost
The total cost of the reef to date, including design
studies, top-up and replacement of damaged containers
is A$2.8M (US$2.1M). This equates to a unit rate of
~A$40/m3.
4.5 Performance
Considerable monitoring of the reef has been carried
out and a number of monitoring reports have been
published (GCCM, 2004). Despite a number of storm
wave events, the reef has proven been effective in
stabilizing the beach and a salient is generally present
(Turner, 2006).
Wave breaking occurs ~50% of the time – generally
for waves >1m at MLWS and >1.8m at MHWS. Good
surf [Figure 9] is experienced regularly on the reef
when wind, waves and tides are suitable. It is noted
that the surf very rarely looks like either the numerical
or physical models as there is often multi-swell / wave
conditions and wind factors. When there is a clean
swell without wind, the modeling is replicated in the
real world.
AUSTRALASIAN CONFERENCE ON COASTS AND PORTS 2007
Figure 9 Surf at Narrowneck (Source ICM)
Prior to initial settlement of the reef [with a crest
height of -0.5m LAT], the reef formed a very hollow
but hazardous wave that often sucked dry at the break
point. Prior to top-ups, when crest heights have been
lower than -1.5m LAT in locations, waves tend to be
more spilling.
It has also been observed that the reef interacts with
the adjacent bar formations, creating more favourable
natural conditions. With the normal sand bars, the
waves tend to break on the reef and then link into the
shorebreak, significantly extending ride length [rides
over 200m have been recorded].
The reef has provided a suitable substrate for
development of a diverse ecosystem and has become a
popular location for fishing and diving. As a result it
has been designated as a no anchoring zone. The type
of geotextile used promotes soft growths [such as
algaes] that do not present a safety hazard to surfers.
4.6 Comments
The following comments and conclusions can be
made:
The project appears to have achieved the objective
of improving surfing conditions when swell, tide
and wind conditions are suitable.
The reef does provide a quality surf wave at times,
but it has not gained a reputation as a great surf
spot. Part of the reason for this appears to be that:
Very high expectations and initial media
‘hype’ followed by negative media.
There are a number of world-class surf breaks
in the area
When conditions favour the reef, a number of
other local breaks work as well
The reef takeoff area is about 250m offshore
[other natural breaks are closer to shore]
Selection of geotextile type influences the type of
marine flora and fauna.
Suitable construction methodology using efficient
gear and experienced operators resulted in a very
low unit cost.
If constructed on a sandy seabed, fluctuations in
the seabed can have significant impacts on reef
“settlement” and performance
Crest levels are important for safety
considerations, although no reports of injuries
have been noted.
Reef generally improves surf quality on adjacent
bars. It is possible for the reef break to link with
the bar break and extend the ride length.
Vessels can damage sand-filled geotextile
containers.
The surface of the reef is now rough. Wave
quality is not affected by hollows it is affected by
isolated high spots.
Despite a number of storm wave events (Hm up to
12m) coastal protection has been effective.
5 Pratte's Reef
5.1 Location and site conditions
Pratte’s reef is located at El Segundo, California. The
wave climate is generally <1m. Tides are semi-
diurnal with a tidal range of approx 1.6m.
5.2 Design
The surfing reef was designed by Skelly Engineering.
The shape [Figure 10] is a delta type with a nose ½
angle of 45deg and crest height of -1.8m MLLW [later
raised to -0.9m MLLW].
Figure 10 Pratte’s design
5.3 Construction materials and methodology
Two types of woven geotextiles were used – polyester
and polypropylene. For safety and budget constraints,
the reef was designed and constructed of ~14t
sandbags that could fit snugly into the back of a
standard tip truck tray. Once filled, they were loaded
onto the barge and towed to site to be placed by a
barge-mounted crane [Figure 11]. Final reef volume
was only ~1,350m3.
Figure 11 Placement of sandbags at Pratte’s
AUSTRALASIAN CONFERENCE ON COASTS AND PORTS 2007
5.4 Costs
The total budget for this project was only US$300,000
(~A$285/m3).
5.5 Performance
Detailed monitoring was undertaken [Borrero and
Nelsen, 2003]. While they noted that Pratte’s has
generally not performed to expectations, there are
some good photos of wave breaking at the reef [Figure
12], and public comments suggest that it is “epic” in
the right conditions [1-5 times per year].
Figure 12 Surf at Pratte’s
Surveys and dive inspections show that seabed
variations and damage to the bags were likely
responsible for significant lowering of the reef,
affecting the wave breaking.
5.6 Comments
The following comments and conclusions can be
made:
The project is generally not seen as successful
There are a number of good surf breaks in the area
Insufficient budget to make the reef of adequate
size.
Seabed fluctations and damaged containers
lowered the reef - major cause of the reduced
effectiveness for surfing
6 Mount Maunganui
Mt Maunganui is located on the west coast of New
Zealand’s north island. Waves are generally <1m high
and tidal range is >2.5m. The reef was designed by
ASR using [small scale] physical and numerical
modeling. It is a basic V shape with a nose ½ angle of
~40deg and a crest height of -0.4m LAT. (see design at
www.asrltd.co.nz)
The reef is being constructed using sand-filled
geotextile containers strapped to a webbing grid in two
halves prior to deployment on the seabed by divers and
filling by a pump powered by a barge-mounted
excavator. As at March 2007, construction has been
very slow due to site conditions and costs [NZ$1.6M]
had been considerably over budget [NZ$0.8M]. The
reef is presently partially covered with a storm bar and
construction is only 80% completed. (see construction
newsletters at www.asrltd.co.nz)
7 Opunake
Opunake is located on the west coast of New
Zealand’s north island. Two reefs are proposed and
construction of the first reef started in March 2006.
The reef is being constructed of large sand filled
geotextile containers filled using a pump and hopper
located on the headland. Construction is presently
awaiting suitable conditions for the construction
methodology. (see design at www.asrltd.co.nz)
8 Conclusions
It is possible to combine coastal protection and
“improved” surf conditions at a reasonable cost.
However, in most cases, public expectations have not
been fulfilled.
In the design, the following issues are important:
Crest height is important for surf, safety and in
determining coastal protection.
The size and location of the reef is important.
Public expectations need to be realistic.
Construction methods need to practical - A very
smooth surface is not necessary, but isolated high
spots should be avoided.
Seabed changes need to be considered.
Numerical modelling tends to overstate the
performance of surf reefs - Wind, wave and tide
range and seabed levels may limit surfability to
certain conditions.
9 References
Bancroft S. 1999. Performance Monitoring of Cable
Station Artificial Surfing Reef. University of WA
undergraduate thesis
Beach Protection Authority. 1986. Hervey Bay
Beaches
Borrero and Nelsen. 2003. Results of a Comprehensive
Monitoring Program at Pratte’s Reef. 3rd International
Surfing Reef Symposium.
DPI. 1999. Report on Major Achievements
GCCM. 2004. Summary of Narrowneck Monitoring to
June 2004. prepared for Gold Coast City Council
Lemme AJ. Hegge BJ. Masselink G. 1999. Offshore
Wave Climate, Perth (Western Australia) 1994 - 96.
CSIRO Marine and Freshwater Research Vol. 50, 2.
Pattiaratchi, C. 1997. Design Studies for an Artificial
Surfing Reef at Cable Station, Western Australia. 1st
International Surfing Reef Symposium
Pattiaratchi, C. 2003. Performance of an Artificial
Surfing Reef: Cables Station, Western Australia.
COPEDEC
Pitt A. 2005. Redgard the Reef Renovator. Artificial
Surf Reef Conference.
Redgard, G. 2006. pers comm.
Turner IL. 2006. Analysis of Shoreline Variability,
Seaasonality and Erosion/Accretion Trends: Feb 06-
July 06. prepared for Gold Coast City Council
AUSTRALASIAN CONFERENCE ON COASTS AND PORTS 2007
Table 1: Reef comparison
SURF "REEF"
PROJECTS
Date
constructed
COUNTRY VOL
[m3]
approx
TYPE total
A$
$/m3
A$
Construction method Tide
Range
[approx]
Average
Wave
climate
Hs
Completed Projects
Bargara 1997 Australia
300 Rock $10,000
$33 Reprofiling existing rocks on
headland with excavator at low
tide
3.7m <1m
Cables 1998- 99 Australia
5,000 Rock $1,400,000
$280 Rock placed with excavator
from barge
0.8m Summer
1-2m
winter
1.5 -
2.5m
Narrowneck 1999-2000 Australia
70,000 SFGC
non-
woven
$2,800,000 $40 150 - 450t mega sand filled
containers filled in hopper
dredge and dropped.
2m 1m
Prattes 1999-01 USA
1,350 SFGC
woven
$385,000 $285 14t sand filled containers
filled on shore, loaded on barge
and placed by crane from barge
1.6m <1m
Partially
Constructed
est
Mount Maunganui 2005 -?? NZ 6,000 SFGC
non-
woven
$1,454,545 $242 mega sand filled containers
attached to web, anchored and
filled in situ
[20% construction outstanding]
>2.5m <1m
Opunake 2006 -?? NZ
? SFGC
non-
woven
$760,000 ?? mega sand filled containers
attached to web, anchored and
filled in situ
[construction stalled?]
>3m
... However, the visual impacts are negligible and, with a suitable orientation and 3D shape, refraction effects can be used to provide a peeling break for surfing as well as energy reduction. A number of reefs have already been constructed to provide surfing benefits (Jackson & Corbett, 2007). ...
... As reef type structures generally need to be constructed from a marine platform rather than directly off the shore, they often have a much higher construction cost than shore-based structures, such as groynes. Advances in design and construction techniques have made multi-functional artificial reefs a feasible cost option for low impact and sustainable coastal protection providing a range of benefits, including surfing, diving and improved marine habitat when suitable materials are used (Jackson & Corbett, 2007). ...
Conference Paper
Full-text available
It is important that management of the coastline in developing areas, particularly rapidly developing areas as the Arabian Gulf, is sustainable, eco-friendly and preserves the coastal amenity. Ideally, structures should be multi-functional and designed to provide amenity and to be safe for users. This paper outlines how multifunctional artificial reefs / breakwaters can be designed to achieve these objectives. Case studies from Gold Coast in Australia and Dubai in the UAE will be presented that show how a multifunctional artificial reef (MFAR) with suitable integrated design and construction methods is one method that can provide sustainable coastal protection with significant environmental and recreational benefits without adverse visual impacts.
... Reefs Despite considerable interest worldwide, only four multi-functional artificial reefs, including Narrowneck, have been completed to date, and the data from these plus data from the two reefs under construction in New Zealand has been analyzed and benchmarked against Narrowneck (Jackson and Corbett 2007). The results, summarized in Table 2, show that Narrowneck has improved surf at a very reasonable unit cost compared to similar reefs. ...
Article
Full-text available
The Narrowneck Artificial Reef is a large submerged structure constructed in 1999-2000 as a key component of the Northern Gold Coast Beach Protection Strategy (NGCBPS) implemented by Gold Coast City Council (GCCC). While primarily a coastal protection structure, its secondary objective was to improve surfing. Since its construction, comprehensive monitoring has been undertaken. To date, the reef has been a success in terms of retaining the wider nourished beach. The structural performance has been satisfactory, with ongoing improvements, and the geotextile has provided a surprisingly good substrate for development of a diverse marine community. In terms of surfing, the reef has achieved its goal and provides improved surfing conditions for a wide range of surf craft. Evaluation of the incidence of wave breaking shows that breaking is initiated on the reef for wave heights over 0.7 m to 2.0 m, depending on the tide. For an average year, waves break on the reef approximately 50% of the time. While waves tend to be more spilling than plunging in average conditions, larger swells, lower tides, and offshore winds have the potential to produce hollow, plunging breakers. The reef needs long period, clean swell to replicate the modelling. As Gold Coast wave conditions are usually bi-modal and often short-crested, there have only been a few examples where this has been the case. Bar formations around the salient also provide favorable conditions on the shore-break and the reef break often merges with the adjacent bar break to extend ride lengths. GPS data shows that recorded rides average 150 to 200 m, but have reached up to 260 to 270 m. Similarly, recorded ride times have reached up to 60 seconds. Despite being home to a number of regular and one-off surfing events, Narrowneck reef has not gained a widespread reputation as a great surf spot. Part of the reason for this appears to be that it is surrounded by world-class surfing breaks and typically these locations work in similar conditions as the reef. The fact that the takeoff area is 300 m offshore also seems to make the reef break less attractive to surfers. Media hype prior to reef construction led to unrealistically high expectations that the reef would perform in all conditions and press statements criticizing the reef before completion has also negatively impacted public perception of its success. While the objective of improved surfing has definitely been achieved, it was not well quantified. While the design has progressively evolved during maintenance works to improve surfing and safety, further improvements specifically improve surfing are not considered warranted.
... ASR Ltd. [14] is one commercial company set up for the purpose of advancing research, testing and constructing ASRs. Researchers have traced the evolution of artificial reefs from empirical and theoretical perspectives [15][16][17], whilst other studies have pro- vided reviews and perspectives of ASRs [3,12,[18][19][20][21] or focused upon specifics such as the use of ASRs to promote surf tourism or coastal protection [10,[22][23][24]. Some monitoring studies have quantified the performance of ASRs objectively [25,26]. ...
Article
The emergence of geotextiles in coastal erosion protection as an alternative material to stone boulders and concrete tetrapods is evident in the recent past. The submergence of geotextiles being colonized by epibiotic organisms on their surface is called marine growth, similar to all other materials inundated in seawater. It includes organisms of the primary producers of algal populations, secondary consumers, and filter feeders of benthic-fouling communities crusting geotextiles' surface. In-situ experimental studies of more than a year of research at a fishing harbour along Chennai coast, India, projected a typical pattern of epibiotic encrustation and its impact on tensile strength nonwoven geotextiles fabrics. Results demonstrated a patchy-mosaic design of marine growth on the geotextile comprising 41 species of sessile invertebrates, including seaweeds, showing a natural succession of biotic density and diversity. Noted distinct stages in colonization were commencing with the domination of deposit feeders, followed by filter feeders, secondary consumers, and primary producers, where later filter feeders subjugated them. The incidence of fundamental ecological succession based on food availability, nature of trophic consumers, and intra/interspecific competition lead to dynamic population shifts on geotextiles. The monolayer settlement pattern of marine growth on the surface is dominated by the benthic filter-feeding community, forming an inverted trophic pyramid structure. Significant differences in tensile strength between geotextile with and without marine growth (p = 0.042) and the progressive improvement in tensile strength indicated no adverse impact on the erosion protection structure's stability. Thus, a harmonious relationship between population density and tensile strength (r = 0.8) represents a mutual relationship between encrusting biota and geotextile substrate, resulting in camouflaging with the coastal background ecosystems as an innovative ecodesign for coastal erosion protection engineering.
Article
Multipurpose Artificial Reefs (MPARs) are structures that may provide aesthetically acceptable coastal protection and improve recreational outcomes. Twenty years after construction of the first MPAR, Narrowneck Reef on the Gold Coast of Australia, most of the available literature is still focused on the planning, design and construction of such structures and peer-reviewed publications on their post-construction monitoring, interaction with sediment transport and impacts on coastal morphology are lacking. The aim of this paper is to evaluate how does Narrowneck Reef influence the sediment transport, and morphological changes around the anthropogenic structure, two decades after construction. To do so, a combination of ten high spatial resolution topo-bathymetric surveys from the top of the dune to the 10 m depth captured over 21 months and a series of 60 simulations using a calibrated numerical model were used. Our results demonstrate that: although not expected during design or reported in similar structures, sand can bypass the MPAR around its offshore end; under oblique waves, the longshore currents are deflected as they pass the reef, resulting in a shadow zone on the downdrift side where sand deposits; the bar crest tends to be higher on the reef's updrift side compared to downdrift, indicating that the MPAR can act as a store for sediments, as initially designed. Furthermore, the MPAR can act to stabilise the bar as it moves onshore with a downdrift offset of the inner bar as a result of low oblique wave incidence. The results presented here demonstrate that the short-term response to the MPAR twenty years after construction is more closely related to the updrift build up of sand and the deflection of longshore currents as they encounter the reef than to the dissipation of wave energy. This is because MPARs are designed to dissipate just enough wave energy so that they can achieve their recreational goal (surfing).
Thesis
Full-text available
The engineering of submerged coastal structures has been improved over the past decade through the inclusion of new functional concepts. In addition to protecting the coast, the submerged structure is able to offer social and economic attractions to the installation site. However, the beach response to submerged coastal engineering is poorly understood. This thesis presents a study of the beach morphodynamic variability with the presence of a submerged structure in the beach system. A natural rocky bank in Reserva Beach (RJ) was the natural reference for the engineering of submerged coastal structures. For this, continuous surveys of field data and physical experiments were carried out on the wave channel in the laboratory. Within a complete seasonal cycle (2015-2016), 26 beach surveys were carried out with topographic (georeferenced leveling) and hydrodynamic monitoring (wave measurement, currents, wave breaking parameters and circulation cells). The results showed that the formation of the wave breaking vector system on the submerged structure geometry determines the coastal protection efficiency, social hazards and public amenity. The results of the physical model showed that the positioning and the strategy using a porous submerged structure on the antinode of the hydrodynamic oscillation of the system has able to activate the formation of a dissipative profile. The field and laboratory databases allow to understand the engineering necessary for an efficient strategy of unite a submerged structure to the dynamics of the beach system.
Conference Paper
Full-text available
INTRODUCTION Globally, the use of rock in coastal design and construction projects has been common practice. This is largely due to the availability of material, relative cost and extensive research and development in rock design. Formulated equations, such as the ‘Hudson’ or ‘van Der Meer’ are used to produce standardized breakwaters, groynes, revetments and offshore reefs, however the structures are typically ‘over designed’, using larger volumes of material than necessarily required for site conditions. With the increase in rock costs globally and specifically in the UAE, this year of 7.00AED/tonne for trucks traveling in the Emirates of Ras Al Khamiah and Fujairah (Shabaan, 2016) coastal projects are becoming increasingly costly and designs should consider more site-specific alternatives with the integration of alternative construction materials, specifically geotextile containers. HISTORY OF GEOTEXTILES IN COASTAL DESIGN There has been significant development of geotextiles in coastal design since their beginning in the 1960’s. International Coastal Management (ICM) has been at the forefront of material and construction methodology development since the early 90’s with the completion of various, successful global coastal projects. Some notable (ICM) projects, utilizing site-specific design and construction methodologies include the following: 1. Narrowneck Artificial Reef, Gold Coast, Australia. Development of new in-situ filling techniques using split hull barge and material strengths for extended durability (15 years since installation). 2. Maroochydore Groyne, Sunshine Coast, Australia. Development of geotextile containers and filling frame for onsite constructability of innovative design. 3. Nearshore Berms, Ullal, India. Development of construction apparatus for efficient methodology. 4. Private Submerged Seawall, Ajman, UAE. Design and construction methodology for the installation of sand filled geotextile containers for emergency erosion protection. Figure 1 Various geotextile containers and methodologies developed by ICM on international projects WHEN TO USE ROCK vs. GEOTEXTILE CONTAINERS Coastal sites vary greatly from location to location and therefore it is highly unlikely that a standardised or ‘textbook’ type solution will be the most site-effective. In some locations the use of both rock and geotextile containers will be more cost/end user efficient, as per recent works in Ajman, UAE (ICM). Some key factors when applying site-specific designs are:  Site Weather Conditions (Wind, Waves, Tides, etc.)  Site Accessibility for Construction  End User Requirements (Beach access, Visual Impact, Environmental Impact, etc.)  Material Supply Costs  Expected Structure Duration Use  Capital vs. Maintenance Costs In some cases, capital costs and construction times can be greatly reduced using temporary geotextile structures to provide an agile coastal solution which can be easily updated/extended/removed etc. as the site requirements and/or coastal processes in the location change. In other cases, rock may be better suited; this may occur when integration into existing structures, greater durability or visual consistency is required. SITE-EFFECTIVE DESIGN As mentioned, there has been significant advancement in the design and construction methodologies of geotextile containers for coastal stabilization. Each site is however unique and requires site-effective design to achieve the most cost and outcome efficient results. Agile designing can enhance and stabilise a coastal location for low capital costs, allowing the site/structure(s) to develop over time as site requirements/conditions change. REFERENCES Shabaan, A. (2016, January 27), Trucks to pay Dh7 for a tonne of rock, Khajeel Times, pp. 7
Article
A variety of patented approaches have been devised in efforts to halt shoreline erosion. Commonly termed ‘alternative’ or ‘innovative’ technologies, these are typically variations on the traditional approaches. A categorization of these approaches is presented that identifies devices placed in the water and devices placed on the beach. These categories are further subdivided. Despite their innovative nature and the claims of their inventors and promoters, these devices suffer from a variety of weaknesses when deployed in the real world. We present a non-exhaustive list of 110 devices for which US patents were awarded since 1970. The view of success of ‘alternative’ devices often differs between reports made by the developer and those of the end-user and only in a few cases have objective assessments been made. Using a variety of sources we review experiences with artificial surfing reefs and beach drainage systems. We conclude that ‘alternative’ devices offer the same range of shortcomings as traditional shoreline stabilization approaches because of the inherent inability to control such a dynamic sedimentary environment and the failure to address the underlying causes of shoreline recession (sea level rise, sediment supply, other engineering structures, and the presence of infrastructure in the active coastal zone).
Article
Multifunctional artificial reefs (MFARs) have been growing in popularity over the last decade. They are offshore submerged structures which provide coastal protection while also enhancing marine and recreational amenities such as surfing and beach widening. A feasibility study was undertaken for São Miguel Island (Azores) where island-wide general site-selection criteria and local site-specific parameters identified São Roque reef as a potential MFAR location. Expert knowledge addressed multidisciplinary aspects through semi-guided interviews, which provided evaluation criteria for the São Roque reef development. Wave changes before and after reef reprofiling were determined using the Regional Coastal Process WAVE propagation model (CEDAS/RCPWAVE). Results demonstrated additional coastal protection to the historic church and existing seawalls, and no adverse effects on the updrift São Roque and downdrift Pó pulo Milicias beaches. Further simulation for an extended reef (30 m seaward) showed model sensitivity together with a greater reduction in approaching wave heights. This analysis suggested that the further seaward the reef is extended, the greater the coastal protection afforded. It also denoted longer, rideable surfing waves and
Conference Paper
Full-text available
Design studies undertaken to investigate the feasibility of constructing an artificial surfing reef, by enhancing an existing surf break, at Cable Station, Western Australia are described. These include physical model tests in a random wave flume and a 1:40 scale model in a 40m x 40m wave basin. The optimum bottom slope, where a plunging wave was present for a range of wave heights and wave periods was found to be 1:20. This is also the natural bottom slope of the study area and is also the slope recorded in many surfing breaks worldwide. Several reef shapes were investigated in the wave basin and a shape that minimises the amount of fill required and that which merges with the existing reef was selected as the final design.
Article
Full-text available
The offshore wave climate of Perth (Western Australia) was analysed by using 2.5 years of non-directional 20-min wave data collected from March 1994 to August 1996. The mean wave conditions are characterized by a significant wave height (Hs) of 2.0 m and a spectral mean wave period (Tm) of 8.8 s. However, considerable annual variation in the wave conditions is experienced because of a distinct seasonality in the regional wind regime. During summer, daily sea breezes generate moderate seas (ambient Hs 1 to 2 m; Tm <8 s). During winter, frequent storms associated with mid-latitude depressions generate heavy seas and swell (ambient Hs 1.5 to 2.5 m; Tm >8 s). A low-amplitude background swell (Hs ~0.5 m), generated distantly in the Indian and Southern Oceans, is present all year round. Analysis of extreme wave conditions (Hs >4 m) indicates that, on average, 30 storms are experienced annually, and the storms are most frequent and intense during July. Estimates of extreme Hs, based on all available offshore wave data (12 years, 1975–96), for 1- and 100-year return periods, are 6.7 m and 9.8 m, respectively.
Performance Monitoring of Cable Station Artificial Surfing Reef. University of WA undergraduate thesis Beach Protection Authority
  • S Bancroft
Bancroft S. 1999. Performance Monitoring of Cable Station Artificial Surfing Reef. University of WA undergraduate thesis Beach Protection Authority. 1986. Hervey Bay Beaches Borrero and Nelsen. 2003. Results of a Comprehensive Monitoring Program at Pratte's Reef. 3 rd International Surfing Reef Symposium.
Design Studies for an Artificial Surfing Reef at Cable Station, Western Australia. 1 st International Surfing Reef Symposium Pattiaratchi, C. 2003. Performance of an Artificial Surfing Reef: Cables Station
  • C Pattiaratchi
Pattiaratchi, C. 1997. Design Studies for an Artificial Surfing Reef at Cable Station, Western Australia. 1 st International Surfing Reef Symposium Pattiaratchi, C. 2003. Performance of an Artificial Surfing Reef: Cables Station, Western Australia.
Redgard the Reef Renovator. Artificial Surf Reef Conference
  • A Pitt
Pitt A. 2005. Redgard the Reef Renovator. Artificial Surf Reef Conference.
Analysis of Shoreline Variability, Seaasonality and Erosion/Accretion Trends: Feb 06July 06. prepared for Gold Coast City Council
  • Il Turner
Turner IL. 2006. Analysis of Shoreline Variability, Seaasonality and Erosion/Accretion Trends: Feb 06July 06. prepared for Gold Coast City Council
Summary of Narrowneck Monitoring to
  • Dpi
DPI. 1999. Report on Major Achievements GCCM. 2004. Summary of Narrowneck Monitoring to June 2004. prepared for Gold Coast City Council Lemme AJ. Hegge BJ. Masselink G. 1999. Offshore Wave Climate, Perth (Western Australia) 1994 -96. CSIRO Marine and Freshwater Research Vol. 50, 2.
Analysis of Shoreline Variability, Seaasonality and Erosion/Accretion Trends
  • I L Turner
Turner IL. 2006. Analysis of Shoreline Variability, Seaasonality and Erosion/Accretion Trends: Feb 06-July 06. prepared for Gold Coast City Council