Shark
predation on the endangered Hawaiian monk seal (Monachus
schauinslandi) is thought to
have had a large impact on the seal population in the
Northwestern Hawaiian Islands (NWHI).
In recent years there has been concern that tiger (Galeocerdo
cuvier) and Galapagos sharks (Carcharhinus
galapagensis)
are killing greater numbers of monk seal pups at French Frigate
Shoals (FFS). Previous
anecdotal observations by National Marine Fisheries Service (NMFS)
and U.S. Fish and Wildlife Service (USFWS) field personnel
suggest that large sharks are common in the summer months at FFS
when many marine animals congregate there to mate and give
birth. In addition,
anecdotal observations by NMFS personnel have led them to
believe that only a few individual sharks are responsible for a
large number of attacks on seal pups.
If these unsubstantiated observations are accurate, then
removal of a small number of sharks could significantly
reduce predation pressure on young seals.
However, more
rigorous scientific evidence is needed to justify such extreme
measures, particularly
within a National Wildlife Refuge.
For example, little attention has been focused on the
movement patterns and site fidelity of these large sharks,
particularly near areas where seals haul out.
This type of information is essential for understanding
the scale of the predation problem and for assessment of the
potential for shark culling efforts to effectively reduce
predation on seals.
The
focus of this research program was to investigate the movement
patterns and site fidelity of large sharks (tiger and Galapagos)
near haul out beaches at FFS using an array of methods:
1) All large sharks were tagged with large, highly
visible identification tags (HVT).
These tags were placed on both sides of the dorsal fin to
facilitate identification of individual sharks by observers on
the shore or in boats.
2) Several tiger
sharks were manually tracked over 6-8 hr periods using standard
telemetry techniques to determine short-term movement patterns.
Tracked sharks were fed
acoustic transmitters to eliminate any trauma associated with
capture and tagging. 3)
Longer-term site fidelity and movement patterns of large sharks
were determined using anchored acoustic monitors.
Sharks were surgically fitted with high-powered,
long-life (2 year battery life) acoustic transmitters.
These transmitters are individually coded to allow
identification of individual sharks detected by acoustic
monitors. Acoustic
monitors were positioned around the major islands of the atoll
and archived data was downloaded from the monitors every three
months.
4) To determine long-range movement, fixed-fin
satellite transmitters were attached to two tiger sharks. Nearly
40,000 detections were recorded on acoustic monitors over a four
year period.
These detections provided insight into the movement
patterns of large sharks at FFS, particularly for tiger sharks.
Much less data was collected for Galapagos sharks.
Restrictions on fishing in prime Galapagos areas and the
culling of individual sharks carrying transmitters severely
hampered attempts to understand the movements and population
demographics of this species.
Repeated
and fairly consistent detections of multiple sharks during our
study offer strong evidence that at least some tiger sharks are
present at FFS throughout the year.
The more sporadic detections of some tiger sharks at FFS,
as well as detections at other islands within the Hawaiian
archipelago demonstrate that some individuals were less
site-attached and moved long distances.
Large tiger sharks spent more time around islands in the
center and southern parts of the atoll during the summer,
particularly East Island.
During winter months sharks spent proportionally more
time around the northern islands (Tern and Trig).
Tiger sharks obviously feed heavily on fledging albatross
at East Island during late spring and early summer.
Monitor data revealed that the appearance of tiger sharks
at East Island is heavily skewed towards the late spring and
early summer months, as well as during early morning hours.
Peak activity of tiger sharks near East Island in terms
of both time of year and the time of day correspond with peak
numbers of fledging albatross.
These data suggest that the movement patterns of tiger
sharks around East Island are heavily influenced by the
availability of this relatively easy to capture food source.
This
project was undertaken under the assumption that the information
gathered would be used to evaluate the potential of a Galapagos
shark-culling program at Trig for reducing seal mortality.
Shortly after we began our study on movement patterns of
sharks, NMFS began killing Galapagos sharks at Trig and also
initiated an “observation study” to quantify shark activity
near Trig through visual observation.
Removal of Galapagos sharks and the increased
restrictions on our fishing protocol limited our ability to
catch Galapagos sharks at Trig and to collect the type of data
that would be useful in addressing our original research
questions. The
shift in research emphasis of movement patterns of Galapagos
sharks near Trig to culling sharks and visual observations had
several immediate impacts on our study.
First, we were no longer able to directly target
Galapagos sharks that were seemingly orienting to seals at Trig.
Second,
the culling project would potentially remove sharks that were
carrying transmitters. Therefore,
not only was our access to the sharks of highest interest (those
at Trig) restricted, but if a transmitter was successfully
deployed in a shark, there was a possibility that the individual
would be killed (and no longer yield any data) when it came near
Trig, the location of highest interest.
The
conditions under which our project was operating were
counterproductive to the successful collection of information
valuable for evaluation of the effectiveness of shark culling on
seal pup survival at Trig Island.
The initial opportunities to investigate interactions
between sharks and seals based on movement patterns of sharks
were squandered, and to date very little information of
substance that could be used to objectively evaluate either the
potential for success, or actual success achieved through the
culling of Galapagos sharks at Trig has been attained.

