SlideShare a Scribd company logo
1 of 1
Download to read offline
The Effects of Anchor Damage and Coral Disease on Sea Fans in the British Virgin Islands
Jessica Perreault1 and Graham Forrester2
1Department of Biological Sciences, 2Department of Natural Resources Science, University of Rhode Island
As the defining feature of the Caribbean’s
underwater infrastructure, coral reefs face a
multitude of physical and environmental
threats1. Gorgonia ventalina, or the common
sea fan, is no exception.
Coral disease: Since the early 1990s, a terrestrial
fungus known as Aspergillus sydowii has ravaged
sea fans throughout the Caribbean, wiping out
huge portions of the population2. When exposed,
healthy sea fans typically increase their
production of melanin - a chemical responsible
for their purple coloring - in an effort to combat
the disease2. This reaction creates a distinct, dark
purple ring around the infected area, effectively
isolating the disease before it can spread.
Aspergillosis will compromise its reproductive
capabilities and eventually kill it2.
Anchor damage from boats: Soft corals like
Gorgonians are fairly delicate and therefore
susceptible to physical disturbances from anchor
damage. The British Virgin Islands are a popular
sailing destination that host over 350,000 tourists
annually, with the majority of guests arriving
between November and March3. Many of these
tourists choose to charter a boat without the
guidance of a captain or a crew, a phenomenon
known as “bareboat chartering”. With little to no
sailing experience, people can rent boats for days
or weeks at a time and sail around the islands.
Many popular sites provide moorings for boats
to stay for the day or overnight. However, the
increasing popularity of these charters has
skewed the ratio of boats looking to moor versus
the number of moorings available. Instead,
charters are forced to anchor at these sites,
causing an irreparable amount of damage to the
reefs4. Although anchoring on coral reef is illegal
in the British Virgin Islands, there is hardly
government effort to enforce the policies.
Most charters simply pick up their anchors and
move to their next destination unscathed,
though the same cannot be said for the reefs
they leave behind.
Objective: We examined the effects of
anchor damage on Gorgonia ventalina
populations in the British Virgin Islands
and tested whether anchor damage
exacerbated the impact of Aspergillus
sydowii on sea fans.
Figure 1. A healthy sea fan (left) is easily distinguishable
from a damaged sea fan (right) based on their coloring. The
damaged fan is a darker shade of purple as a result of
increased melanin production. This is a common response
for a threatened immune system much like the human
body produces a fever in response to the common cold.
Disease Dynamics Unchanged Despite a Strong Anchoring Impact
The graphs below show the direct effect of anchoring on sea fans and on
the symptoms of sea fan disease. High and low anchoring sites were
compared using ANOVA, with environmental variation minimized by
grouping geographically and physically similar sites (a “block” effect).
To Everyone Who Contributed
For funding, the National Science Foundation; For fieldwork support, Lianna Jarecki and Rebecca Flynn; For expert opinions, many 
BVI boat captains, dive instructors and environmental professionals; For logistical support, the Guana Island staff and Dive BVI. 
For photo credit, David Gleeson and Rebecca Flynn. Thank you all for your support!
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
High Low
DiseasePrevalence
Anchor Damage
0
10
20
30
40
50
60
70
High Low
SeaFanSize(cm)
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
High Low
PopulationDensity
Figure 6A.
Population Density –
Number of sea fans per m2
Areas of low anchorage
experienced a higher density of
sea fans, while sea fans found in
areas of high anchoring were
much more sparsely distributed.
Figure 6B.
Sea Fan Size –
Average height per fan
Areas of low anchoring had
significantly larger sea fans. The
average heights differed from 39.5
cm in highly damaged sites to 55.2
cm in less damaged areas.
Figure 6C.
Disease Prevalence –
Percent of sea fans infected
Prevalence of Aspergillosis was
fairly consistent across field
sites, regardless of damage
condition. This contradicts our
initial hypothesis.*
Threats to Sea Fans on Coral Reefs
Assessing the Damage
1.0m
30.0 m
Sea fan Algae Coral
Site Area Transect
Figure 4A. (Below) A diagram of a standard
hypothetical 30-meter transect, looking from
above. All sea fans within a 1 x 30 m strip
were recorded. Figure 4B. Transect
tapes were placed
haphazardly around
each dive site. Up to
four tapes were placed
at each site.
Figure 4C. Sea fans
exhibiting varied levels
of injury from anchors
were recorded at each
site. Fans knocked over
or uprooted were
classified as dead.
Figure 3. To isolate the
effects of anchoring, we
chose 21 sites to collect
the initial data. Each
site was then assessed
for their level of anchor
damage. Dive sites
were assessed based on
topographical
similarities. Sites in
close proximity
typically featured
similar underwater
landscapes and were
scored in the same
groups.
Figure 5. To measure the
presence of disease, we
recorded height, width,
damage status, disease
severity (percent cover of
disease), and indication of
immunoresponse (melanin
ring width) of sea fans
within each 30-meter
transect.
References
1 "Global Coral Reef Monitoring Network (GCRMN)." International Coral Reef Initiative. United Nations Environment Programme, 1 Jan. 2014. Web. 1 Nov. 2014. <http://www.icriforum.org/gcrmn>.
2 Kim, Kiho, and C. Drew Harvell. "The Rise and Fall of a Six‐Year Coral‐Fungal Epizootic." The American Naturalist 164.S5 (2004): S52-63. Web of Science. Web. 19 July 2014.
3 "Latest Statistics 2013." One Caribbean. Caribbean Tourism Organization, 26 June 2014. Web. 1 Nov. 2014. <http://www.onecaribbean.org/wp-content/uploads/6AUGLattab13.pdf>.
4 Forrester and Flynn, Unpublished manuscript
5 Jolles, A., Sullivan, P., Alker, A., & Harvell, C. (2002). Disease Transmission Of Aspergillosis In Sea Fans: Inferring Process From Spatial Pattern. Ecology, 83(9), 2373-2378.
6 Troeger, Victoria J., Paul W. Sammarco, and John H. Caruso. "Aspergillosis in the Common Sea Fan Gorgonia Ventalina: Isolation of Waterborne Hyphae and Spores."Diseases of Aquatic Organisms 109 (2014):
257-61. Print.
7 Toledo-Hernández, C., Yoshioka, P., Bayman, P., & Sabat, A. (2009). Impact of disease and detachment on growth and survivorship of sea fans Gorgonia ventalina. Marine Ecology Progress Series, 393, 47-54.
Low
Why is Aspergillosis equally successful across sites of
varied population dynamics?
To date, researchers have determined that the prevalence of this disease is most
successfully spread via two potential pathways5:
Primary contact Secondary contact
Diseased sea fans must be very Disease spores can detach from
close or touching in order to transmit infected fans and spread to
the infection. fans within a short range.
How does Aspergillosis spread in high anchoring areas?
This study revealed that the disease is equally prevalent across the BVIs
regardless of damage status (Figure 6C). However, based on what we know
about the spread of Aspergillosis, sparsely distributed sea fans should not be as
susceptible to hosting this pathogen.
One potential explanation for this gap in
understanding may be linked to the presence
of the waterborne disease spores6.
Secondary transmission may still occur at
high anchoring sites, but instead of naturally
detaching from infected fans, disturbance from
anchors could be a mechanism for detaching
the live spores more readily.
A future study could investigate the hypothesis that anchoring accelerates the
secondary transmission of Aspergillosis.
Is anchoring or disease responsible for smaller fans?
Most studies on this subject have concluded that this pathogen typically targets
larger fans, and therefore should not be as successful in areas with smaller
targets. But many of these studies use sea fan mortality as a proxy for disease
severity over time, which can be misleading7. The reality is that sea fans, large
or small, are equally susceptible to Aspergillosis. Small fans have an enhanced
immune response relative to their larger counterparts, so they are able to fend
off the disease for longer. Large fans die off more quickly as a result.
This study observed that areas of high anchoring have a lower mean fan size.
We now hypothesize that the effect of anchors killing off larger fans negates the
size-dependent rate of mortality from Aspergillosis. The timeline below
suggests one potential explanation for the size discrepancy found in areas of
high anchoring exposure.
The option of either primary or
secondary transmission provides a
potential explanation for the success of
Aspergillosis in areas of low anchor
damage, where fans are distributed
fairly close together (Figure 6A). This
spatial arrangement is ideal for the
spread of this disease. 	
  
Aspergillosis
spores are
disturbed by
anchors and
secondarily
transmitted to fans
across the reef.
Neighboring
fans of all sizes
become
infected.
Smaller fans have a
stronger immune
response relative to
larger fans. Larger
diseased fans die off
more quickly.
High anchoring
areas experience
an eventual shift
in mean size of
sea fan
population.
Height
Width
%Cover of
disease
Melanin
ring
width
Figure 2. Bareboat charters anchored in Muskmelon
Bay on Guana Island. Most of landscape beneath
them is made up of coral reefs.
*Although not represented graphically, other symptoms of the disease (severity,
immunoresponse, etc.) all showed similar consistencies when compared to sites of
high and low anchor damage.

More Related Content

Similar to Poster Final

SCANU B129829-Final Project Report
SCANU B129829-Final Project ReportSCANU B129829-Final Project Report
SCANU B129829-Final Project Report
Simona Scanu
 
Evidence for impacts by jellyfish on north sea
Evidence for impacts by jellyfish on north seaEvidence for impacts by jellyfish on north sea
Evidence for impacts by jellyfish on north sea
ratupura
 
GEOG336_Campbell_Final_Draft
GEOG336_Campbell_Final_DraftGEOG336_Campbell_Final_Draft
GEOG336_Campbell_Final_Draft
Benjamin Campbell
 
ANDREW TONGUE SCCS15 POSTER
ANDREW TONGUE SCCS15 POSTERANDREW TONGUE SCCS15 POSTER
ANDREW TONGUE SCCS15 POSTER
Andrew Tongue
 
David Moreton Dissertation Abstract
David Moreton Dissertation AbstractDavid Moreton Dissertation Abstract
David Moreton Dissertation Abstract
David Moreton
 
California Mussels Influence On Mytilus Californianus
California Mussels Influence On Mytilus CalifornianusCalifornia Mussels Influence On Mytilus Californianus
California Mussels Influence On Mytilus Californianus
Stacey Wilson
 
Background Sea otters are one of the few cute and cuddly creature.pdf
 Background Sea otters are one of the few cute and cuddly creature.pdf Background Sea otters are one of the few cute and cuddly creature.pdf
Background Sea otters are one of the few cute and cuddly creature.pdf
shakeelkhan911
 
pink seafan 2015 marine policy
pink seafan 2015 marine policypink seafan 2015 marine policy
pink seafan 2015 marine policy
Jean-Luc Solandt
 
2016 Vianna et al. Indicators of fishing mortality in Palau_Authors copy
2016 Vianna et al. Indicators of fishing mortality in Palau_Authors copy2016 Vianna et al. Indicators of fishing mortality in Palau_Authors copy
2016 Vianna et al. Indicators of fishing mortality in Palau_Authors copy
Gabriel Maciel de Souza Vianna
 

Similar to Poster Final (20)

SCANU B129829-Final Project Report
SCANU B129829-Final Project ReportSCANU B129829-Final Project Report
SCANU B129829-Final Project Report
 
Research Proposal - Are the Adélie penguin, Pygoscelis adeliae, populations w...
Research Proposal - Are the Adélie penguin, Pygoscelis adeliae, populations w...Research Proposal - Are the Adélie penguin, Pygoscelis adeliae, populations w...
Research Proposal - Are the Adélie penguin, Pygoscelis adeliae, populations w...
 
EFFECT OF SOUND POLLUTION ON FISHES
EFFECT OF SOUND POLLUTION ON FISHESEFFECT OF SOUND POLLUTION ON FISHES
EFFECT OF SOUND POLLUTION ON FISHES
 
Does Moderate Ocean Noise Disrupt Foraging?
Does Moderate Ocean Noise Disrupt Foraging?Does Moderate Ocean Noise Disrupt Foraging?
Does Moderate Ocean Noise Disrupt Foraging?
 
Evidence for impacts by jellyfish on north sea
Evidence for impacts by jellyfish on north seaEvidence for impacts by jellyfish on north sea
Evidence for impacts by jellyfish on north sea
 
Science-2015
Science-2015Science-2015
Science-2015
 
Report
ReportReport
Report
 
GEOG336_Campbell_Final_Draft
GEOG336_Campbell_Final_DraftGEOG336_Campbell_Final_Draft
GEOG336_Campbell_Final_Draft
 
SymposiumPoster
SymposiumPosterSymposiumPoster
SymposiumPoster
 
ANDREW TONGUE SCCS15 POSTER
ANDREW TONGUE SCCS15 POSTERANDREW TONGUE SCCS15 POSTER
ANDREW TONGUE SCCS15 POSTER
 
David Moreton Dissertation Abstract
David Moreton Dissertation AbstractDavid Moreton Dissertation Abstract
David Moreton Dissertation Abstract
 
Environmental impact of fishing and carbon footprinting due to fishing
Environmental impact of fishing and carbon footprinting due to fishingEnvironmental impact of fishing and carbon footprinting due to fishing
Environmental impact of fishing and carbon footprinting due to fishing
 
Speech
SpeechSpeech
Speech
 
California Mussels Influence On Mytilus Californianus
California Mussels Influence On Mytilus CalifornianusCalifornia Mussels Influence On Mytilus Californianus
California Mussels Influence On Mytilus Californianus
 
DUMO Algacleaner english
DUMO Algacleaner englishDUMO Algacleaner english
DUMO Algacleaner english
 
Background Sea otters are one of the few cute and cuddly creature.pdf
 Background Sea otters are one of the few cute and cuddly creature.pdf Background Sea otters are one of the few cute and cuddly creature.pdf
Background Sea otters are one of the few cute and cuddly creature.pdf
 
pink seafan 2015 marine policy
pink seafan 2015 marine policypink seafan 2015 marine policy
pink seafan 2015 marine policy
 
2016 Vianna et al. Indicators of fishing mortality in Palau_Authors copy
2016 Vianna et al. Indicators of fishing mortality in Palau_Authors copy2016 Vianna et al. Indicators of fishing mortality in Palau_Authors copy
2016 Vianna et al. Indicators of fishing mortality in Palau_Authors copy
 
Poster AIL - Ultrasound as control strategy for bryozoans
Poster AIL - Ultrasound as control strategy for bryozoansPoster AIL - Ultrasound as control strategy for bryozoans
Poster AIL - Ultrasound as control strategy for bryozoans
 
Ocean Noise: What we Learned in 2006
Ocean Noise: What we Learned in 2006Ocean Noise: What we Learned in 2006
Ocean Noise: What we Learned in 2006
 

Poster Final

  • 1. The Effects of Anchor Damage and Coral Disease on Sea Fans in the British Virgin Islands Jessica Perreault1 and Graham Forrester2 1Department of Biological Sciences, 2Department of Natural Resources Science, University of Rhode Island As the defining feature of the Caribbean’s underwater infrastructure, coral reefs face a multitude of physical and environmental threats1. Gorgonia ventalina, or the common sea fan, is no exception. Coral disease: Since the early 1990s, a terrestrial fungus known as Aspergillus sydowii has ravaged sea fans throughout the Caribbean, wiping out huge portions of the population2. When exposed, healthy sea fans typically increase their production of melanin - a chemical responsible for their purple coloring - in an effort to combat the disease2. This reaction creates a distinct, dark purple ring around the infected area, effectively isolating the disease before it can spread. Aspergillosis will compromise its reproductive capabilities and eventually kill it2. Anchor damage from boats: Soft corals like Gorgonians are fairly delicate and therefore susceptible to physical disturbances from anchor damage. The British Virgin Islands are a popular sailing destination that host over 350,000 tourists annually, with the majority of guests arriving between November and March3. Many of these tourists choose to charter a boat without the guidance of a captain or a crew, a phenomenon known as “bareboat chartering”. With little to no sailing experience, people can rent boats for days or weeks at a time and sail around the islands. Many popular sites provide moorings for boats to stay for the day or overnight. However, the increasing popularity of these charters has skewed the ratio of boats looking to moor versus the number of moorings available. Instead, charters are forced to anchor at these sites, causing an irreparable amount of damage to the reefs4. Although anchoring on coral reef is illegal in the British Virgin Islands, there is hardly government effort to enforce the policies. Most charters simply pick up their anchors and move to their next destination unscathed, though the same cannot be said for the reefs they leave behind. Objective: We examined the effects of anchor damage on Gorgonia ventalina populations in the British Virgin Islands and tested whether anchor damage exacerbated the impact of Aspergillus sydowii on sea fans. Figure 1. A healthy sea fan (left) is easily distinguishable from a damaged sea fan (right) based on their coloring. The damaged fan is a darker shade of purple as a result of increased melanin production. This is a common response for a threatened immune system much like the human body produces a fever in response to the common cold. Disease Dynamics Unchanged Despite a Strong Anchoring Impact The graphs below show the direct effect of anchoring on sea fans and on the symptoms of sea fan disease. High and low anchoring sites were compared using ANOVA, with environmental variation minimized by grouping geographically and physically similar sites (a “block” effect). To Everyone Who Contributed For funding, the National Science Foundation; For fieldwork support, Lianna Jarecki and Rebecca Flynn; For expert opinions, many BVI boat captains, dive instructors and environmental professionals; For logistical support, the Guana Island staff and Dive BVI. For photo credit, David Gleeson and Rebecca Flynn. Thank you all for your support! 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 High Low DiseasePrevalence Anchor Damage 0 10 20 30 40 50 60 70 High Low SeaFanSize(cm) 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 High Low PopulationDensity Figure 6A. Population Density – Number of sea fans per m2 Areas of low anchorage experienced a higher density of sea fans, while sea fans found in areas of high anchoring were much more sparsely distributed. Figure 6B. Sea Fan Size – Average height per fan Areas of low anchoring had significantly larger sea fans. The average heights differed from 39.5 cm in highly damaged sites to 55.2 cm in less damaged areas. Figure 6C. Disease Prevalence – Percent of sea fans infected Prevalence of Aspergillosis was fairly consistent across field sites, regardless of damage condition. This contradicts our initial hypothesis.* Threats to Sea Fans on Coral Reefs Assessing the Damage 1.0m 30.0 m Sea fan Algae Coral Site Area Transect Figure 4A. (Below) A diagram of a standard hypothetical 30-meter transect, looking from above. All sea fans within a 1 x 30 m strip were recorded. Figure 4B. Transect tapes were placed haphazardly around each dive site. Up to four tapes were placed at each site. Figure 4C. Sea fans exhibiting varied levels of injury from anchors were recorded at each site. Fans knocked over or uprooted were classified as dead. Figure 3. To isolate the effects of anchoring, we chose 21 sites to collect the initial data. Each site was then assessed for their level of anchor damage. Dive sites were assessed based on topographical similarities. Sites in close proximity typically featured similar underwater landscapes and were scored in the same groups. Figure 5. To measure the presence of disease, we recorded height, width, damage status, disease severity (percent cover of disease), and indication of immunoresponse (melanin ring width) of sea fans within each 30-meter transect. References 1 "Global Coral Reef Monitoring Network (GCRMN)." International Coral Reef Initiative. United Nations Environment Programme, 1 Jan. 2014. Web. 1 Nov. 2014. <http://www.icriforum.org/gcrmn>. 2 Kim, Kiho, and C. Drew Harvell. "The Rise and Fall of a Six‐Year Coral‐Fungal Epizootic." The American Naturalist 164.S5 (2004): S52-63. Web of Science. Web. 19 July 2014. 3 "Latest Statistics 2013." One Caribbean. Caribbean Tourism Organization, 26 June 2014. Web. 1 Nov. 2014. <http://www.onecaribbean.org/wp-content/uploads/6AUGLattab13.pdf>. 4 Forrester and Flynn, Unpublished manuscript 5 Jolles, A., Sullivan, P., Alker, A., & Harvell, C. (2002). Disease Transmission Of Aspergillosis In Sea Fans: Inferring Process From Spatial Pattern. Ecology, 83(9), 2373-2378. 6 Troeger, Victoria J., Paul W. Sammarco, and John H. Caruso. "Aspergillosis in the Common Sea Fan Gorgonia Ventalina: Isolation of Waterborne Hyphae and Spores."Diseases of Aquatic Organisms 109 (2014): 257-61. Print. 7 Toledo-Hernández, C., Yoshioka, P., Bayman, P., & Sabat, A. (2009). Impact of disease and detachment on growth and survivorship of sea fans Gorgonia ventalina. Marine Ecology Progress Series, 393, 47-54. Low Why is Aspergillosis equally successful across sites of varied population dynamics? To date, researchers have determined that the prevalence of this disease is most successfully spread via two potential pathways5: Primary contact Secondary contact Diseased sea fans must be very Disease spores can detach from close or touching in order to transmit infected fans and spread to the infection. fans within a short range. How does Aspergillosis spread in high anchoring areas? This study revealed that the disease is equally prevalent across the BVIs regardless of damage status (Figure 6C). However, based on what we know about the spread of Aspergillosis, sparsely distributed sea fans should not be as susceptible to hosting this pathogen. One potential explanation for this gap in understanding may be linked to the presence of the waterborne disease spores6. Secondary transmission may still occur at high anchoring sites, but instead of naturally detaching from infected fans, disturbance from anchors could be a mechanism for detaching the live spores more readily. A future study could investigate the hypothesis that anchoring accelerates the secondary transmission of Aspergillosis. Is anchoring or disease responsible for smaller fans? Most studies on this subject have concluded that this pathogen typically targets larger fans, and therefore should not be as successful in areas with smaller targets. But many of these studies use sea fan mortality as a proxy for disease severity over time, which can be misleading7. The reality is that sea fans, large or small, are equally susceptible to Aspergillosis. Small fans have an enhanced immune response relative to their larger counterparts, so they are able to fend off the disease for longer. Large fans die off more quickly as a result. This study observed that areas of high anchoring have a lower mean fan size. We now hypothesize that the effect of anchors killing off larger fans negates the size-dependent rate of mortality from Aspergillosis. The timeline below suggests one potential explanation for the size discrepancy found in areas of high anchoring exposure. The option of either primary or secondary transmission provides a potential explanation for the success of Aspergillosis in areas of low anchor damage, where fans are distributed fairly close together (Figure 6A). This spatial arrangement is ideal for the spread of this disease.   Aspergillosis spores are disturbed by anchors and secondarily transmitted to fans across the reef. Neighboring fans of all sizes become infected. Smaller fans have a stronger immune response relative to larger fans. Larger diseased fans die off more quickly. High anchoring areas experience an eventual shift in mean size of sea fan population. Height Width %Cover of disease Melanin ring width Figure 2. Bareboat charters anchored in Muskmelon Bay on Guana Island. Most of landscape beneath them is made up of coral reefs. *Although not represented graphically, other symptoms of the disease (severity, immunoresponse, etc.) all showed similar consistencies when compared to sites of high and low anchor damage.