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Okaloosa County BOCC — June 2, 2015 — Okaloosa Co ABF Feasibility Study C2014-042 — reading text
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an average of 43 months while windward buoys survive an average of 25 months — a 40%
reduction in expected longevity. One would anticipate that the periodic storm exposure with winds
exceeding 40 mph in the GOM would further reduce buoy longevity. As such, the proposed program
should implement design changes to account for the rougher conditions.
The Hawaii program found that the single spherical spar buoy design (Figure 5) provided the
best performance while minimizing losses. Figure 5 shows a typical Hawaii FAD surface buoy system.
The system consists of a 200-lb (400 kg) 4.8-ft diameter steel spherical spar buoy with 3,000 lbs (1,400
kg) of positive displacement. The 3.5-ft mast atop the float holds a light system and 7-ft pipe welded
below the float provides a counterweight to maintain the buoy upright. About 100 ft of 13 mm chain
attaches the buoy to the rope mooring system. Sections of negatively buoyant and positively buoyant
nylon rope provide an inverse catenary or “slack” (“S” shape) mooring system. The nylon rope and
mooring system provide the slack needed to absorb cyclic loading on the mooring as the surface buoy
heaves in the waves and ensures that the lower part of the mooring will not drag on the ocean bottom as
might happen with a conventional catenary system. Three 1,700-lb concrete block anchors attached to 80
ft of 13 mm chain deployed in a tripod configuration provides the anchor system for the buoy.
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Figure 5. Single Spherical Spar Buoy Design (figure provided by HIMB, SOEST, University of Hawaii)
This buoy and anchor system typically costs an average of $8,000 – $9,000 to build and install
offshore Hawaii with the nylon rope being the highest single component cost at approximately $2 per foot
($2,000 – $20,000 for 700 – 10,000 ft). Ship time for installation ranges from $7,000 – $8,000 per day.
Simultaneous installation of multiple buoys allows significant cost savings resulting in the average cost of
$8,000 – $9,000 to build and install. Notably, Hawaii buoy installation sites generally lay 5 – 20 miles
from land, which reduces ship travel time for the installation. In comparison, a relatively small (3m)
discus buoy (similar to the discus buoys used by NOAA to mount oceanographic instrumentation in the
area of interest) may cost approximately $20,000 for just the buoy. The mooring system may cost
between $10,000 – $50,000 depending on the water depth (200m – 800m) and installation in the proposed
project area may cost approximately $20,000 – $40,000 depending on the total number of buoys proposed
and the distance offshore. The increased mooring and installation costs primarily result from the larger
buoy(s) imparting increased forces on the mooring system and requiring larger or more specialized
vessels for deployment. From the information above, the water depth appears to be the greatest
controlling factor for both the discus and spar buoy structures.
Based on the research cited, the typical failure mechanisms of the Hawaii buoy system result
from near-surface shackle connections (i.e., failure due to the rapid movements and friction damage near
the surface) or rope breakage. Rope breakage is believed to be caused by cyclical loading resulting from
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increased wave and currents, barnacle growth, and/or shark or other sharp-tooth fish biting the ropes.
From conversations with Hawaii researchers, vessels mooring to the buoy system also decrease the
structure life by increasing the loading on the mooring line and connection hardware. Notably, a
correlation between depth and longevity was not apparent from the Hawaii FAD system. Similarly,
typical failure mechanisms of NOAA buoys in the GOM generally result from severing of the synthetic
line either through deliberate or accidental vandalism. In fact, from discussions with the National Data
Buoy Center (NDBC) staff, they have begun installing camera systems on the frequently damaged buoys
to deter vessels from mooring to the buoy. Connection hardware failure is generally less of a concern
because the buoys and/or mooring systems are typically replaced every 3 – 5 years.
Equipping the surface buoy with a GPS tracking system will allow easy relocation of the
equipment should the connection system fail. However, the anchoring system can only be reused if it is
retrieved from the bottom using specialized surface vessels equipped with cranes and underwater
autonomous vehicles. Given the proposed water depth of 1,000 ft or greater, the cost of retrieving the
anchoring system will likely be cost prohibitive.
A small-scale (1 – 3 buoys) installation in the GOM (~40 – 60 miles to the site) with a more
robust buoy system designed to survive moderate GOM storms may cost $20,000 – $30,000 per buoy (to
build and install). This estimate is primarily based on a preliminary scaled-up version of the Hawaii
system (larger anchors, chain, and rope) with a large diameter, round (spar) buoy. The availability of
large-scale commercial vessels (capable of performing multiple deployments in a single trip) may greatly
affect the cost estimate. Designing the structure to provide a platform for scientific instrumentation or
vessel mooring (larger discus buoy and mooring system) presents additional design challenges. Given the
distance offshore, the vessels mooring to the structure will likely be 50+ ft in length and the County will
have little to no control over the number or size of vessels mooring to the structure. Such vessels may also
attempt to anchor to the structure during increased wave/current events exponentially increasing the
loading on the structure and connection hardware. Vessels moored to the structure also pose increased
damage potential to any equipment that may be mounted on the surface buoy (e.g., solar panels,
navigation lights, scientific/environmental monitoring equipment, etc.). Designing the structure to
withstand the potential loading cases associated with vessel mooring will greatly increase the structure
cost and increase the potential for structure failure (reduced structure life). The increased damage
potential with a mooring structure will also likely require additional monitoring and buoy inspections,
increasing the maintenance costs of the structure(s). Comparing the relatively simplistic, low-cost Hawaii
buoy system with typical (higher-cost) NOAA buoys, the County should first install a small-scale buoy
network similar to the Hawaii system. The County can make design modifications to future deployments
based on 1 – 2 years of monitoring data from the original system. Further, because deep-water buoy
systems are prone to failure, the County should consider the purchase of a buoy system (buoy, mooring,
and anchor) designed as a unit. This may provide the greatest amount of confidence in optimal buoy
lifespan.
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5.0 BUOY LOCATIONS
Given the scope of this preliminary study, we do not propose specific locations for a proposed
buoy system. However, we provide the following items for consideration when planning the proposed
buoy network.
• Target Fish Species — Figures 2 and 3 provide essential fish habitat maps for two
primary target species (billfish and tuna). Additionally, available literature indicates these
species prefer variations in water temperature and depth that typically occur along and
within the De Soto Canyon.
• Water Depth — based on information presented in the previous section, the depth of
water will likely greatly affect the initial material costs.
• Distance Offshore — the County should consider the distance offshore of the buoy
system, specifically for proposed use (e.g., recreational fishing), installation and
maintenance costs, local preference, etc.
• Bureau of Ocean Energy Management (BOEM) lease areas — as discussed below,
placing the buoys in offshore federal waters will likely require a permit and/or consent of
use agreement from BOEM. If the proposed buoy area is already leased, obtaining
additional use agreements from the BOEM leasee may present additional difficulties for
installation and maintenance of the system. However, relatively few active leases exist in
the area of interest for placing buoys.
• Buoy spacing — technical literature suggests 4 – 8-mile spacing between buoys in the
Hawaiian system has been successful for effective fish attraction. Some research
(reported in Dempster and Kingsford, 2003) indicates that fish orient to FADs spaced up
to 18 km (approx. 12 miles) apart. Tuna may orient to anchored buoys from a distance of
10 km (Leroy et al., 2013).
• Additional uses — the County should also consider utilizing the buoys (or a single buoy)
as a platform for oceanographic or ecological monitoring equipment. Utilizing the
buoy(s) as a research platform may reduce the initial and maintenance costs through
research partnerships; however, including this equipment may also increase the overall
cost of the buoy and mooring structures (i.e., larger buoy and anchoring system).
Much of the deeper GOM bottom has been leased to members of the energy industry for oil, gas,
and other mineral exploration and extraction. BOEM manages these leases and regulates mineral
resources in Federal waters. Many active leases exist in the northern Gulf of Mexico, but relatively few
lie within the project area of interest and should be easily avoidable (Figure 6). Regardless, the County
will still likely be required to coordinate with BOEM regarding the installation of the buoy system.
Considering only the target fish species and water depth, the County should consider placing
buoys near the northern tip of the De Soto Canyon and atop the West Florida Shelf along the eastern edge
of the De Soto Canyon.
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90°0'0"W 89°0'0"W 88°0'0"W 87°0'0"W 86°0'0"W 85°0'0"W 84°0'0"W
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One Inch = 40 Nautical Miles
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OKALOOSA COUNTY,
FLORIDA
