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Goliath grouper is the largest of the western north Atlantic groupers. It can reach about 455 kg (800
lbs) and over 2 m total length. The following features can easily distinguish goliath grouper: broad
head, round tail, small eyes, and short dorsal spines. They tend to have a brownish-yellow or
greenish-gray mottled pattern and small black spots on their fins. Fish mature at 5 or 6 years of age at
about one meter in length. They are relatively long lived, with individuals at least 37 years old found in
exploited populations. It is possible, however, that older fish occurred in unfished populations. This
species is very vulnerable to cold temperatures and red tide (see threats section below).

Historically, goliath grouper were found in tropical and subtropical waters of the Atlantic Ocean, both
coasts of Florida, and from the Gulf of Mexico down to the coasts of Brazil and the Caribbean. Most
adults are found on shallow reefs, the deepest being about 150 feet. They form spawning
aggregations of about 100 individuals at consistent sites from July through September. Fish may
move up to 100 km from inshore reefs to these spawning sites, which typically occur on rock ledges,
isolated patch reefs, and even on ship wrecks. Aggregations declined in the 1980's due to overfishing.

Goliath grouper have a pelagic larval duration of approximately 6 weeks. They settle in shallow
mangrove habitat, first in mangrove leaf litter, and then along mangrove shorelines. The juvenile
stage lasts 5 or 6 years in this mangrove habitat, after which fish egress to shallow reefs, eventually
joining adult populations offshore. Their distribution in mangroves depends on local water quality,
particularly dissolved oxygen content (> 4 ppm) and mid-range salinities (> 10 ppt).



Goliath grouper are particularly susceptible to overexploitation. This is due in part to their slow
growth, longevity, and large size at sexual maturity. In addition, because they aggregate to spawn,
they are easy targets. This is true for any species in which large numbers of otherwise
widely-dispersed fish become concentrated in predictable areas and times. Fishing on spawning
aggregations increases catch per effort to the point of population collapse, removing reproductive
individuals that are usually the largest fish in the population. Indeed, intense recreational and
commercial fishing pressure contributed to the population decline of goliath grouper in the 1980s.
Similar fishing-induced declines have occurred on spawning aggregations of Nassau grouper
Epinephelus striatus, gag Mycteroperca microlepis, and other grouper species throughout the world.
Mangrove Habitat Loss

Juvenile goliath grouper recruit to mangrove habitat throughout their range. This habitat in Florida
has declined since the early 1900s due to channelization to redirect freshwater flow from the
Everglades, mosquito-abatement, and development for agricultural, industrial, and residential
purposes. Most of the existing mangrove habitat in the entire United States occurs along the west
Florida coast. Very little mangrove habitat remains on the southeast coast. Because mangroves serve
as important juvenile habitat for these fish, their loss could affect population recovery even if
reproductive levels of adult fish are high.

Red Tide

Red tide effects on goliath grouper are being evaluated at the National Marine Fisheries Service
Laboratory. Information available on the following site: http://www.sefsc.noaa.gov/redtidegrouper.jsp.

Vulnerability of the Goliath Grouper Population in Florida




Goliath grouper, a large reef fish with populations in tropical Atlantic waters, is vulnerable to
overexploitation and local extinction and is classified by the World Conservation Union (IUCN) as
critically endangered throughout most of its range. Yet populations in southeastern U. S. waters are
recovering after 20 years of protection afforded by the South Atlantic and Gulf of Mexico Fishery
Management Councils and Florida Fish and Wildlife Conservation Commission when they closed the
fishery in 1990.  The question is: can managers in Florida ignore the global status of this species?

As scientists who have studied this species for over a decade and a half and reviewed the literature
and reports of colleagues and other scientists throughout the world (e.g., Bullock et al. 1992, Sadovy
and Eklund 1999, Frias- Torres 2006, Koenig et al. 2007, Felix-Hackradt and Hackradt 2008, Brusher and
Schull 2 009, Craig et al. 2009, Gerhardinger et al. 2009, Mann et al. 2009, McLeanachan 2009, Murie et
al. 2009, Graham et al. 2009, Evers et al. 2009, Cass-Calay and Schmidt 2009), we say no. The
science-free perceptions and very vocal pronouncements of various groups about the biology,
behavior, and population status of this species, while loud and strong, should not trump the best
available scientific evidence in making management decisions. Our objective in this brief document is
to juxtapose the scientific evidence following from this body of research with the most pervasive
opinions voiced in the southeastern United States.

The Opinion: Goliath groupers compete directly with recreational reef fish fishermen for and
substantially reduce the populations of groupers and snappers on reefs in south Florida.

The Science: There are two lines of evidence against this view provided by dietary and trophic
studies of goliath grouper and videographic surveys of the distribution and abundance of reef fish on
reefs off southwest Florida, the center of goliath grouper abundance. In the stomach contents of over
200 goliath groupers sampled from South Florida we found no groupers and very few snappers. Only
three percent of the prey items were snappers, and these were all gray snappers occurring in the
mangroves in close proximity to the juvenile goliath grouper
Stomach contents represent prey eaten just prior to capture, or a short-term view of diet (Figures 4
and 8). However, for an understanding of diet over the long term, and goliath grouper's position in
the food web (i.e., trophic level) we used stable isotope analysis (Koenig and Coleman 2009). Results
showed a relatively low position in the food web, similar to that of South Florida pinfish (Lagodon
rhomboides; Chasar et al. 2005). Thus, goliath grouper must typically feed on lower trophic level
species, not on those species occupying higher trophic levels, such as groupers and snappers.

In our reef surveys of southwest Florida, we found a significant positive relationship between the
number of snapper (all species combined) and the number of goliath groupers present on surveyed
sites; that is, the higher the number of goliath grouper occupying a reef, the higher the number of
snappers on that reef (Figure 5). We found no significant relationship between the number of adult
goliath grouper and the number of individuals of other groupers on the same sites. These data
support the diet studies showing that few if any snappers and groupers are eaten by adult goliath
grouper. Further, we found that most of the snappers and groupers on sites with goliath groupers
were smaller than the minimum-fishery-size limit which suggests either that goliath grouper, if they do
eat these fish, concentrate only on those exceeding the minimum size limit, or alternatively, that the
fishery itself is responsible for removal of economically important species.

The Opinion: Goliath grouper compete directly with lobster fishermen by eating many lobsters in
South Florida.

The Science: Our stomach content data, sampled from goliath grouper in areas of high lobster
abundance, provide strong evidence against this view. Using the same stomach content data, we
found only one lobster (less than 1% of the dietary items). The diet consisted mostly of crabs and
slow-moving bottom-dwelling fishes such as toadfish.

The fact is that lobsters are preferred prey for many species, including sharks, rays, triggerfish, and
grouper (including goliath grouper). When determining the impact of a predator on a particular prey
population, however, the question is not what can the predator eat, or even, what prey does the
predator prefer? The appropriate question is: what does the predator eat within an ecological
context?

The supposition that lobster form an important component of the goliath grouper diet follows from a
report written by Jack Randall (Hawaii Biological Survey) about reef species sampled from the West
Indies in the 1960s (Randall 1967). In this report, Randall indicated that a high percentage of the
goliath grouper diet consisted of spiny lobsters. At that time (1959 - 1961) and in that place (St. John ,
VI), lobsters were abundant (Randall, personal communication), so the observation of goliath grouper
feeding on them is not surprising. But between 1960 and about 1998, lobster landings tripled
throughout the region, including Florida (FAO 2001). Today, in many areas of the Caribbean, lobster
populations are severely overexploited while there are limited data about population health,
abundance, and fisheries to help inform fishery management practices (FAO 2009). In the Florida
Keys, where the fishery for lobsters is intense, it is doubtful that goliath grouper can affect the fishery
catch significantly, and our data support this view.

The Opinion: Goliath grouper, because of their large size, require huge amounts of food to survive
and eat indiscriminately, reducing biodiversity on reefs.

The Science: While it is true that adult goliath grouper are large, they are also extremely sedentary,
rarely leaving home sites except to migrate to spawning sites. Their method of predation is to sit and
wait for prey, and then use a suction method, common to all groupers and many other reef fish, to
draw prey into their mouths.

To estimate the food consumption rate of goliath grouper, we developed a bioenergetics model.
While the model is preliminary, it shows that adult goliath grouper require only small amounts of food
for maintenance (Figure 6) because of their low metabolic rates and slow growth rates, which become
progressively slower as the fish increase in size.

If goliath grouper ate everything on the reef, we would expect to see lower biodiversity with higher
goliath grouper abundance. However, the exact opposite is true. Our data indicate that biodiversity is
higher overall in areas with greater numbers of goliath grouper; that is, the relationship between the
number of fish species and the abundance of goliath grouper is a positive one

The Opinion: Our reefs are "out of balance"; goliath grouper have to be "thinned out" to regain that
balance.

The Science: Many Florida reefs are out of ecological balance. Indeed, this is a world-wide
phenomenon that is related to the combined effects of overfishing, coastal development, pollution,
and climate change, not to the presence of goliath grouper. Altered ecological balance will not be
regained by reducing the abundance of goliath grouper, a native species that is recovering from
intense overfishing, but by allowing other overfished species to recover while attempting to reduce a
variety of human-induced impacts. Those fishers with decades of experience on Florida reefs know
this to be true. It is the newcomers with less experience who perceive overfished reefs as "normal".
Scientists call this phenomenon "shifting baselines" because the perception of "normal" changes
with each successive generation.

The Opinion: Goliath grouper are dangerous to divers.

The Science: Our observations suggest that the frequency of goliath grouper bites is vanishingly
small. We have interacted directly with over 5000 adult goliath grouper in the water, and have tagged
over 2100 large individuals with spearguns. During all these interactions, we have experienced only a
single harmless nip on the hand by one individual that we had cornered under a ledge and were
harassing intensely to try to induce it to produce sounds (booms) for our underwater hydrophone
recordings.


Some divers have reported being bitten by goliath grouper. In most cases, the diver had a stringer of
speared fish that were the likely target of the grouper, rather than the diver. However, considering
that goliath grouper have very small teeth and a very weak bite (they feed by sucking prey into their
mouths, not by biting it, like a shark), the worst wound that could be inflicted by a goliath grouper
would amount to scratches, not serious injuries.

The Opinion: There must be a periodic kill of hundreds of adult goliath grouper to obtain data on size,
age, and reproductive condition necessary for stock assessment.

The Science: None of these data require the destruction of the fish. All can be obtained through
careful sampling of individuals.

Size is a simple measure to obtain non-destructively. We do this underwater with a video camera
mounted with a double laser system. The laser system produces beams that are adjusted to be
parallel. With the camera and lasers on, the beams are projected onto the sides of a fish oriented
perpendicular to the beams (Figure 9). Later, in the lab, the fish can be measured because the
distance between the laser dots projected onto the fish is known.

Age is most often determined from fishery catches by removing otoliths (concretions similar to
limestone in the ear chambers of fish; otoliths function in equilibrium and hearing) from individual
landed fish. However, age can also be determined non-lethally from dorsal fin rays (Figure 10). These
cartilaginous rays can be cut from the fish after it is captured; the fish can then be tagged and
released unharmed, and the removed fin rays grow back in several months. Like otoliths, fin rays lay
down annual rings, similar to the rings of a tree, and these can be used to age the fish. Murie et al.
(2009) have published on the use of dorsal fin rays for goliath grouper aging.

We have received considerable support from recreational and commercial fishermen interested in
participating in non-consumptive research projects that involve use of non-destructive sampling of
goliath grouper (Figure 11). This type of project would provide a considerable amount of data on
regional age and size structure, data on regional and seasonal diet, and movement data because
captured fish could be tagged before releasing them. As an added bonus, this volunteer program
would provide an opportunity for researchers to educate the fishermen on the recent scientific
research on goliath grouper and further dispel the myths circulating within the fishing community.


While the goliath grouper population is in recovery, the current status is unknown, as is the potential
impact of removals of hundreds of adult fish. Certainly the opportunity to educate fishermen in
general marine ecology and goliath grouper biology and conservation practices should far outweigh
the completely unnecessary destruction of individuals.

Reproductive data can also be collected from goliath grouper non-lethally, and economically to
provide stock assessment biologists with the necessary information to assess recovery of the stock.
To determine reproductive state, sex, and sexual pattern (e.g., gonochorist or hermaphrodite), we
take gonad biopsies by inserting a small tube into the genital opening and vacuuming out a small
piece of the gonad tissue. This tissue is then prepared for viewing under the microscope to
determine reproductive condition. It is also possible to estimate the mass of the ovary in females in
spawning condition and, coupled with spawning frequency, estimate fecundity. Spawning frequency is
estimated non-destructively on the aggregations by using methods discussed in Mann et al. (2009). In
brief, fish were externally tagged with a short-interval depth-sensing tag and monitored for several
weeks. Because spawning fish ascend above the reef, the spawning frequency of an individual can
be determined directly by the frequency of female ascents.

We also can estimate directly the reproductive output and timing of spawning by collecting eggs
using an array of nets deployed downstream from spawning sites, as we have done off the Atlantic
and Gulf coasts of Florida.  Details of the spawning behavior and timing of goliath grouper spawning
can be found in Mann et al. (2009).

Discussion:

Goliath grouper is a native species that evolved on reefs on both sides of the Atlantic over millions of
years. It is a natural and integral component of Florida's reef ecology and thus is not disruptive to the
reef community. Truly disruptive species include such non-native species as the Indo-Pacific lionfish
(Pterois volitans), a species introduced to western Atlantic in the early 1990s. Lionfish are active
predators of newly recruiting fish to native reefs, wreaking havoc on reef populations (Albins and
Hixon 2008). Part of the problem is the absence of checks and balances on lionfish population
expansion through control by predators or other factors. Yet there are few eradication plans for this
species because the economic impact has not been determined.

All the scientists who have studied the behavior and ecology of goliath grouper acknowledge their
optimism over the ongoing recovery of this species in Florida. Other fish species similarly fished to
economic extinction have not fared so well. For example, the giant sea bass (Stereolepis gigas)
population of the Eastern Pacific has not recovered despite nearly 30 years of limited protection.
(http://www.arkive.org/black-sea-bass/stereolepis-gigas/info.html). This species is similar to goliath
grouper in that it is large and feeds primarily on crabs and slow-moving fishes.


Still, the optimism is guarded because the level of goliath grouper recovery remains unknown and the
time trajectory for complete recovery uncertain. A key element in recovery of goliath grouper
populations in Florida is the availability of high-quality mangrove habitat in southwest Florida (Koenig
et al. 2007, Koenig and Coleman 2009). Juveniles spend their first 5 to 6 years of life in this habitat and
it was here in the juvenile population that the first signs of recovery appeared (Cass-Calay and
Schmidt 2009).

Optimism is also dampened by the fact that the south Florida ecosystem has been altered to such a
high degree over the last 100 years (Ogden et al. 2005), that suitable mangrove nursery in all
probability presents a bottleneck to the production of this species (Koenig et al. 2007). Also, losses
due to release mortality and illegal harvest result in continued overfishing (Porch et al. 2006).
Because of these issues and the inherent vulnerability of goliath grouper to fishing pressure, caution
should be the hallmark of any management decision. The fact that a number of very vocal people
consider goliath grouper a nuisance species speaks worlds about the poor job we have done
collectively as scientists and managers to educate the public about marine systems. The fact that
managers would seriously consider destructive sampling of a species known to be critically
endangered elsewhere in their range suggests adherence to political rather than ecological or
conservation principles.


The goliath grouper was listed as a candidate species to the Endangered Species List in 1991
throughout its geographic range in U. S. waters--an area extending from North Carolina southward
through the Gulf of Mexico. All harvesting of the goliath grouper in federal waters of the
southeastern United States (including the Gulf of Mexico) has been prohibited since 1990 and in the
Caribbean since 1993. Recovery of populations will be indicated when both the age and size structure
and the geographic range are reestablished. Until then, some level of protection will likely always be
required, based on the life history characteristics that make them susceptible to rapid overfishing in
the first place--longevity, slow to mature, aggregating to spawn.

The National Marine Fisheries Service, under the authority of the Magnuson-Stevens Fisheries
Conservation and Management Act, continues to list the goliath grouper as overfished in Reports to
Congress on the Status of Fisheries. Commercial or recreational retention of goliath grouper is
prohibited both by the South Atlantic Fisheries Management Council and the Gulf of Mexico Fisheries
Management Council in their snapper-grouper and reef-fish fishery management plans

Goliath Grouper have been overexploited to the point of economic extinction. It was in large part due
to public testimony of commercial fishers on the status of the fishery that resulted in protection for
this species by the Gulf of Mexico and South Atlantic Fishery Management Councils. At this point, the
level of recovery in the EEZ (Exclusive Economic Zone or 200-mile Limit) is uncertain. Evaluation of
the dynamics of spawning aggregations by visual and acoustic methods could provide a basis for
monitoring recovery. That is, if goliath grouper abundance in spawning aggregations is a correlate of
stock size, then these fishery-independent methods can be used efficiently to monitor recovery. The
benefits of recovery may well extend into additional commercial enterprises, particularly ecotourism
as opportunities to view these magnificent fish in their natural habitat increases. With the help of the
Florida Wildlife Research Institute (see FWRI Hotline), we are developing a catalogue of goliath
grouper sightings throughout the southeastern United States. These efforts so far have concentrated
in Florida, but we are slowly obtaining information from other sites. Periodic updates will be made to
this distribution map.