Summary of " Status and Trends of Bermuda Reefs and Fishes : 2016"
Murdoch TJT (201 8 ) Status and Trends of Bermuda Reefs and Fishes: 2016 Report Card. BREAM: Bermuda Reef Ecosystem Analysis and Monitoring Programme Report, Bermuda Zoological Society, Flatt’s. Bermuda. Bermuda Biodiversity Project #266
Link: Here
Synopsis
Coral reefs provide vital protection of
Bermuda’s shores from storms, and attract the people who support Bermuda’s
thriving tourism and international business economies. This report presents the
findings of the second year of comprehensive monitoring surveys of fish
stocks and coral reef condition across the entire Bermuda Platform, since 2010,
at 39 sites distributed across 4 zones: Inner Lagoon, Outer Lagoon, Rim Reef
and 10-m Forereef, by the Bermuda Reef Ecosystem Analysis and Monitoring (BREAM)
Long-term Ecological Monitoring (LTEM) programme. We used the newly developed
IUCN GCRMN Caribbean reef monitoring protocol, and international standard for
fish and reef monitoring. The GCRMN protocol focuses on various kinds of
information about local reefs and reef fish populations:
1.
Fish abundance and biomass of
commercially-exploited predatory fishes, plant-eating (herbivorous) fishes and
other fish groups.
2.
Benthic assemblage structure:
cover of hard corals, fleshy macroalgae and other sessile reef organisms.
3.
Abundance of juvenile hard corals
and coral diseases that influence the future condition of reef corals.
4.
Abundance of mobile meso-faunal
invertebrates such as lobsters, plant-eating sea urchins and other reef
animals.
In this report, we utilize a four-component
index of reef condition, called the Sea Life Index (SLI), which we introduced
in 2016 in the report on the “Baseline
Status of Bermuda’s Reefs and Fishes” (Murdoch and Murdoch 2016). We compared
our baseline data from the same 39 sites to new data collected in the summers
of 2015 and 2016, using a team of trained scientific divers. Each reef was
surveyed with replication using standardized scientific methods. The results of
the 2016 monitoring assessment are summarized below, ranked by the strength of
their potential impact.
Main Conclusion
The Sea Life
Index (SLI) for the Bermuda reef ecosystem as a whole region, shown below,
remains Fair.
The SLI for each
reef zone are shown below. SLI, and each component factor, improves as the
distance from shore of each zone increases. This implies that human factors are
in part driving reef condition, and, since policy and resource management is
focussed on human behaviours, that reef condition can be improved though
management and conservation in ways that would improve reef health.
Critical |
Poor |
Fair |
Good |
Very Good |
Positive Results
Status |
Regional Trend |
Action |
|
Sea Life Index |
Fair |
↔ |
YES |
Herbivorous Fishes – Biomass |
Very Good |
↑ |
NO |
Invasive Lionfish - Abundance |
Very Good |
↔ |
NO |
Hard Corals –
Cover |
Good |
↔ |
NO |
Crustose
Coralline Algae, Turfs, Bare Rock (CTB) – Cover |
Good |
↔ |
NO |
Juvenile Hard
Corals |
Fair |
↔ |
NO |
·
Overall, the SLI is Fair, but
Stable. This indicates that reef and fish health across the four zones of the region
should be improved, through directed marine resource management, while the
ecosystem still retains the natural capacity for improvement.
·
Herbivorous Fishes were found
to be in Very Good (very abundant) and increasing condition across the region,
and were seen to be in higher densities in the Outer Lagoon, Rim and 10-m
Forereef zones in 2016 relative to 2015 and the Baseline surveys. Bermuda’s two
decades of protection of parrotfishes, following the 1990 fish pot ban, seems
to be working. Surgeonfishes protection should also be considered, since these
unregulated fish species are large and abundant enough to be the target of
harvest.
·
Invasive Lionfish were not
observed in any of the 37 sites in 2016. This Very Good (absent) status contrasts
sharply with most Caribbean countries. For example, lionfish were observed in
over 25% of reef sites across the Mesoamerican region when using the same
survey methods (Healthy Reefs Initiative 2017). The rarity of lionfish in
Bermuda. specifically in shallow water reefs where juvenile parrotfish have
their strongest impact to reef health, is very positive news. Eddy et al (2016)
determined that juvenile parrotfishes are not a major component of the diet of
Bermuda lionfish. Additional analysis of the BREAM LTEM data of juvenile
parrotfish abundance may further illustrate the lack of ecological impact by
lionfish across the shallow reef platform.
·
Hard Corals remain in Good (high)
cover in 2016, with little change from 2015 or the Baseline surveys. Hard
Corals rely on the other reef factors to remain resilient to change.
·
CTB was generally in Good (high)
cover, but did decline on the 10-m Forereef zone. However, since Hard Corals
were observed to increase in 2016 in the same zone, the reduction in CTB may be
a natural consequence of this otherwise beneficial change to the 10-m Forereef
habitat.
·
Juvenile Corals were Fair
(moderately abundant) and unchanging over the survey periods. Positive news.
Negative Results
Factor |
Status |
Regional
Trend |
Action |
Predatory Fishes – Biomass |
Critical |
↔ |
YES |
Territorial Damselfishes – Abundance |
Poor |
↑↑↑ |
YES |
Herbivorous Snails & Hermit Crabs – Abundance |
Critical |
↓↓↓ |
YES |
Herbivorous Sea Urchins – Abundance |
Critical |
↔ |
YES |
Coral Diseases & Bleaching – Prevalence |
Poor |
↔ |
YES |
Fleshy Macroalgae – Cover |
Poor |
↔ |
YES |
·
Predatory Fishes remain in
Critical (very low) condition across the platform, due to overfishing. These
fishes play a vital role in maintaining the condition of the ecology of
Bermuda’s coral reefs. Management actions to reduce the catch and increase the
protection of large and mid-sized groupers, snappers and sharks, should be a
national priority.
·
Territorial Damselfish are in
Poor (high) abundance in 2016, and have increased substantially and
significantly since both the Baseline surveys and 2015. Their biomass has
doubled in Lagoon since Baseline. This needs to be addressed by improving
stocks of snappers and mid-sized groupers (i.e. meso-predatory fishes) on
lagoonal reefs. We also recommend that the relationship between territorial
damselfishes, the coral they harm, and the meso-predatory fishes that keep
territorial damselfishes in check be assessed further. It may also be useful to
close fishing on 2 to 4 lagoonal patch
reefs for 2-3 years, to see if a reduction in human fishing pressure allows the
recovery of meso-predatory fishes and a subsequent reduction in the abundance
of coral-damaging territorial damselfishes.
·
Microherbivorous Snails and
Hermit Crabs were in Critical (low) condition, declining substantially in 2015
and more so in 2016 relative to Baseline surveys. The microherbivores maintain
crustose-coralline algae habitat, which is critical for the recruitment of new
hard corals. An increase in predation or in mortality caused by disease or
pollution may have caused the decline. Focused surveys of the important
Microherbivore group should be done as soon as possible across the Rim and 10-m
Forereef zones.
·
Herbivorous Sea Urchins were
observed to remain in Critical (very low) condition in 2016, with an additional
decline in abundance on the 10-m Forereef. It may be that predation has increased
on this now rare group of sea urchins, and we recommend adding sea urchin
predators such as triggerfishes to the fish assessments in future surveys. In
addition, echinoderms including sea urchins often are very patchily distributed
on the scales of 100-m to 10-km. Large-scale drift surveys across the Rim and
10-m Forereef zones, which document the location and extent of high-density
patches of sea urchins are advised.
·
Coral Disease was seen to be
Poor (high) in both the Rim and 10-m Forereef, with substantial increases in
coral disease in the Rim reef zone. It is recommended that further study on the
dynamics and changes in coral disease in these zones be carried out as soon as
possible.
·
Fleshy Macroalgae remains in
Poor (high) condition in 2016, and was seen to be significantly higher in the
Inner Lagoon zone compared to Baseline and 2015. Inner Lagoonal reefs are in
particularly poor condition. Further research into the ecology of these nearshore
lagoonal reefs is required to determine the specific causes of damage and how
to resolve them.
Recommendations for Action
The following recommendations are based on
the condition of each factor (above) assessed in the project:
1.
The restoration of grouper and
snapper stocks, their enhanced protection, and improved management of all
predatory fishes and sharks, to prevent future declines should be a national
priority.
2.
Determine whether macroalgae
continues to increase in cover within the Inner Lagoon, and the causes for its
increase.
3.
Further study of the dynamics
and changes in coral disease in Bermuda should be carried out as soon as
possible.
4.
The relationship between
territorial damselfishes, the coral they harm, and the meso-predators that keep
territorial damselfishes in check be assessed further. It may also be useful to
close fishing on a very small number of lagoonal patch reefs for 2 to 4 years,
to see if a reduction in human fishing pressure allows the recovery of
meso-predatory fishes, and a subsequent reduction in the abundance of
coral-damaging territorial damselfishes.
5.
Add sea urchin predators to the
fish assessments in future surveys. In addition, echinoderms including sea
urchins often are very patchily distributed on the scales of 100-m to 10-km.
Large-scale drift surveys across the Rim and 10-m Forereef zones, which
document the location and extent of high-density patches of sea urchins is
advised.
6.
Focused follow-up surveys of
the important Microherbivore group be undertaken as soon as possible across the
Rim and 10-m Forereef zones.
Additional Recommended Management Actions or Changes
to Policy
In addition to the recommendations above, we recommend
that the following management strategies are implemented:
A: Support the Monitoring of
Coral Reefs and Fishes
This report represents Bermuda’s national assessment
of the condition of our coral reefs and fishes, as part of the international
Global Coral Reef Monitoring Network assessment of reefs across the Caribbean.
The project was partially funded by two non-government grants by the Bermuda
Zoological Society and the XL-Catlin End-to-End Marine Research Grant. However,
the project was only possible through the donation of a substantial amount of
time and resources by the BREAM programme and the Murdoch and Gosling families.
The Bermuda Government has committed to the protection
and management of Bermuda’s coral reefs and marine resources through the
creation of policy and via its commitments to several local and international
conventions, including the Bermuda Biodiversity Action Plan, the Convention on
Biological Diversity, the Convention of Migratory Species, and the Convention
of Wetlands of International Importance.
As such, future monitoring of the status and condition
of fishes and coral reefs should be supported and funded, at least to some
extent, by the Bermuda Government.
B. Support the Development of
an Environmental Decision-Making Protocol
Changes in each factor assessed within this BREAM LTEM
project should function as indicators that are directly linked to specific
management and conservation actions. It would be preferable that Government and
Non-Government stakeholders assisted in the development of an Environmental
Decision-Making Protocol (EDMP) that defined what actions were available and
appropriate responses to changes in the abundance or distribution or status of
each of the critical reef health indicators we assess in this report. The
development of an EDMP would accelerate the rate at which resource managers and
conservationist could respond to problematic changes in the condition of our
reefs or fish stocks, and would provide nationally accepted goals for marine
environmental health and resilience.
C: Restoration of Predatory
Fish Populations
1.
Enhance the stocks of groupers
by introducing a limited ban on the capture and sale of Black groupers during
their spawning period (as we currently do with spiny lobster), based on
evidence of the timing of their maximum aggregation at spawning sites.
2.
Consider bag and size limits on
grey snappers, schoolmaster snappers, yellowtail snappers, graysbys and coneys.
3.
Expand our knowledge of
juvenile predatory fish habitats, which are generally within the lagoon (patch
reefs), along the shore (nearshore), and within enclosed bays (inshore). Many
species of offshore reef fish, including predatory fish species, start life by
settling as juvenile fish to coastal habitats, only to move offshore as they
mature.
4.
Reduce coastal development and
pollution impacts to the marine environment, as many juvenile reef fishes are
found the inshore and nearshore waters first before they move to outer reef
areas.
5.
Design coastal structures such
as docks and breakwaters with rough surfaces or attachments, which mimic
natural habitat, so that they provide additional habitat for juvenile and adult
fishes.
6.
Restore coastal mangroves,
rocky intertidal and seagrass habitat, which all has declined substantially in
the past 75 years.
D. Expand Marine Spatial Protected
Areas
Protected areas act as a marine resource “banks” and
provide “interest” in the form of continuously available fishes for commercial
and recreational harvest, through the spill-over effect, and enhanced
reproductive output. We recommend the expansion in the distribution of
protected areas that span the reef platform from inshore bays, along lagoonal
chains of reefs, out to the forereef. These areas are juvenile habitats that
are current threatened due to a lack of smaller predatory fishes and high
damselfish densities. Networks of protected reefs allow fish to transition from
zone to zone throughout their life cycle, by providing protected paths from
nearshore habitats to the lagoon, rim and forereef.
E. Expand the Fishing
License Programme
Recently the Fishing License programme was expanded to
include recreational spear fishers. We recommend that all recreational fishers
require a licence. This would include both those fishing from the shore and
those using marine craft. Access to fishing activity should not be financially
onerous to those with low income, however. No-cost licences to locals who use
hand lines within their parish of residence could be provided so that the
financially challenged retain access to fishing activities.
F. Recommendations for Environmental
Organizations
Many of the recommended actions within this report are
also within the range of issues addressed by local environmental organizations.
We hope that these recommendations are adopted by local stakeholders. We offer
our services in providing the members of local non-government organizations
with lectures and information that supports the sharing of information on how
to better manage and improve the condition of Bermuda’s coral reefs.
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