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Coral reef fish represent a broad range of ecological types
and vary considerably in their economic importance. Almost without exception
these diverse taxa have a pelagic larval stage, which lasts for weeks
to months. After settlement from the plankton, most of these species are
relatively site-attached and often associated with particular reef habitats.
The pelagic larval stage may function as a mechanism for colonizing patchily
distributed habitats or unpredictable environments while spreading the
risk of local extinction across a wide geographical range. Thus, at large
spatial scales (10's to 1000's of km) reef fish communities can be classified
as open non-equilibrial systems where spatially divided sub-populations
are inter-connected via larval dispersal. The degree of connectivity among
reef systems and its importance to fish population regulation is largely
unknown.
A recent paper in the journal Science (Roberts 1997) modeled larval transport
envelopes based on general surface current patterns and the average larval
duration in an attempt to establish the connectivity of Caribbean coral
reefs. Despite criticism that oceanographic processes were oversimplified
the model provided a basis for testing specific hypotheses regarding the
sources and sinks of larval supply and illuminates the need to link up
management initiatives where international boundaries cut across potential
envelopes of larval transport. Between 1998 and 2000 CMES tested the degree
of larval connectivity of fishery resources between the US and British
Virgin Islands with a project funded by the University of Puerto Rico
Sea Grant College Program. The two year project to identify the spatial
and temporal patterns of larval fish supply and settlement was part of
a collaborative effort with the International Center for Living Aquatic
Resources Management's (ICLARM) Eastern Caribbean office located in Tortola,
BVI.
The importance of this study becomes apparent when one becomes familiar
with the biology of reef fishes. The arrival and recruitment of these
larval fishes is the primary mechanism for replenishing our fish populations.
Thus understanding the patterns of larval fish distribution and settlement
is extremely important in maintaining our fishery resources. One of the
major difficulties in studying larval biology is that larvae are patchily
distributed in the plankton and settlement is often episodic and synchronized
with the lunar cycle. The correspondence between the abundance of pelagic
larvae, their distribution in the plankton and subsequent settlement patterns
requires sampling a collaborative research program conducted at large
spatial and temporal scales. Our study determined seasonal and annual
variation in larval supply and settlement at three spatial scales: between
islands (10-1000 km, Tortola, St. Thomas, Jamaica), between reefs (1-10
km, 3 reefs per island) and within reefs (0.1-1 km, three traps per reef).
Larval supply was measured using larval fish light traps constructed of
1/4" plexiglass mounted in an aluminum frame (dimensions: 40 cm x
40 cm x 50 cm). A battery-powered miniature fluorescent light (8 watts)
was mounted on the top of each light trap in a waterproof tube and a plastic
tub with 0.5 mm mesh was mounted on the bottom to concentrate the catch.
Monthly sampling was conducted during seven consecutive nights around
the new moon at three sites on each island.
During the new moon period of June to September 1999 three light traps
were set near each of three fringing reefs in the British Virgin Islands
(BVI) and the United States Virgin Islands (USVI). Separation between
traps, reefs and islands was 0.1 km, 2-5 km and 50-60 km, respectively
and the BVI sites were upcurrent from the USVI sites. The three sites
in the US and British Virgin Islands are shown in Figure 1.

Figure 1. British and United States Virgin Islands, shown with the
six study sites marked, (Note the outlying islands of Anegada (British)
and St. Croix (United States) are not shown on this map).
Catches varied substantially among traps, sites and months. Hierarchical
cluster analyses of total catches showed sites within islands usually
grouped together each month. Sample catches from sites within the BVI
and USVI were clearly distinct (Figure 2) . In the BVI, the largest numbers
of almost all taxa were caught consistently at one site. This site, a
proposed marine protected area, may be a local 'hotspot' for settlement.
Peak abundance of each family generally coincided at BVI sites. By contrast,
in USVI no one site consistently produced more fish and abundances of
several families peaked at different sites in different months.

Figure 2. Dendrograms for cluster analysis (using average linkage)
of total family abundance divided by number of light traps set for June
- September 1999. Note Flay Cay and Sprat Bay were not sampled in June.
Mean light trap catch rates over time for the eight most abundant families
showed that for individual taxa, considerable variation existed in both
the temporal and spatial supply between regions, but also between sites
within regions. Furthermore, the overall processes appear to act differently
in BVI and USVI. For example, in BVI, the largest pulse of six out of
the eight most abundant families was found at Hans Creek. Peak abundance
of each family generally coincided at BVI sites, with September being
the month of greatest abundance for most families. By contrast, in USVI
abundances of several families peaked at different sites and supply of
larvae appears more uniformly distributed over the months July - September.
For three families, abundance was particularly different between BVI and
USVI. In September, 36.6, 2.4 and 4.3 snappers per trap were caught at
the three sites in BVI, while USVI yielded only 0.1, zero and 0.4. Snappers
were also relatively abundant at BVI sites in July and August, but were
virtually absent from USVI samples for all months. For surgeonfish the
pattern reversed, with 0.1, 0.9 and 0.8 fish caught from BVI sites in
September compared with 27.6, 11.5 and 10.5 from USVI sites. Surgeonfish
were more abundant at USVI sites in July and August than at BVI sites.
Similarly, jacks were notably less abundant in all months at BVI sites
compared to USVI.
Our results suggest variation in the taxonomic composition of supply
of larvae appears to cause the different patterns between and within BVI
and USVI, rather than variation in the overall abundance of a set assemblage
of species. We noted that two of the three families showing the greatest
differences between USVI and BVI were deep-bodied fish. At the largest
scale, the strong separation of BVI and USVI sites in the cluster analysis
argues against the notion of a single source of fish larvae operating
over the whole 50-60 km distance, at least during our surveys. Roberts
(1997) considered passive dispersal of fishes and grouped USVI, BVI and
Puerto Rico within a single 'one month dispersal envelope'. However, he
noted the limitations of this approach and suggested that actual interaction
distances might be smaller when active fish behavior was considered.
If the differences we observed at the 50-60 km scale were caused by sequential
depletion as larvae from a single upstream source passed over the islands'
reefs, fewer fish of all species would be expected in the down stream
area. Further, a consistent spatial pattern of relative abundance might
even be expected at sites within each region. Alternatively, if larval
fish settling on BVI and USVI reefs come from separate sources or active
behaviors cause markedly different distributions of larvae, a more haphazard
pattern in both numerical abundance and species composition is expected.
This is the pattern that emerges.
Thus, while we cannot pinpoint sources for the larvae caught during our
surveys, our results support the growing body of evidence that reef fish
supply of larvae may be strongly variable over only a few kilometers,
and quite different assemblages of fish may be supplied to reefs tens
of kilometers apart. Such variation may reflect different sources of larvae
supplying reefs at this scale, or a greater degree of local retention
than was previously thought plausible. If the latter, supply of larvae
to the reefs of the BVI and USVI may be less dependent on each other than
previous research suggests.
Watson, M. & R.S. Nemeth (ms in prep). Spatial and temporal distribution
patterns of coral reef fish larvae in the Virgin Islands archipelago.
Roberts, C.M. 1997. Connectivity and management of Caribbean coral
reefs. Science 278: 1454-1457.
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