11th ICRS Abstract book - Nova Southeastern University

11th ICRS Abstract book - Nova Southeastern University 11th ICRS Abstract book - Nova Southeastern University

24.12.2012 Views

7-5 Coral Yellow Band Disease; Current Status in The Caribbean, Outbreaks And The Links To New Indo-Pacific Lesions Angela RICHARDS DONA* 1 , J.M. CERVINO 2,3 , Vicky KARACHUN 2 , Elizabeth LORENCE 2 , Erich BARTELS 4 , Konrad HUGHEN 5 , Garriet SMITH 6 , Thomas GOREAU 7 1 Biological Sciences, Pace University, Brooklyn, NY, 2 Biological Sciences, Pace University, NY, NY, 3 Geochemistry, Woods Hole Oceanographic Inst., Woods Hole, 4 Mote Marine Lab, Summerland Key, FL, 5 Geochemistry, Woods Hole Oceanographic Inst., Woods Hole, MA, 6 Biological Sciences, University of South Carolina, Aiken, SC, 7 Global Coral Reef Alliance, Cambridge, MA Yellow band disease (YBD) has had a severe impact on the major reef building corals in the Caribbean. Recent data from Lesser Antilles indicates that this
 disease is still in a severe epidemic phase showing similar trends compared to the late 1990s. Ten meter belt transects taken at varied depths of Montastraea spp. indicate high indices of yellow band lesions. At 5m depth, the largest number of live Montastraea spp. were found. Yellow band rings and lesions were positively identified to be affecting an average of 8.4 (79%) colonies per transect. Only an average
of 2.2 (21%) colonies in this depth range appeared healthy. At 10m depth Montastraea colonies which could be positively identified with distinct YB lesions seem to be more numerous than at deeper depths. An average of 1.2 (16%) healthy colonies and 6.2 (84%) colonies affected by YBD per 10m transect were counted. At 15m there
was an average of 1.2 (44%) healthy colonies and 1.5 (56%) colonies affected by
YBD per 10m transect. These data coincide with recent severe outbreaks in the Indo Pacific where identical lesions were found on the surfaces of Diploastrea spp., Herpolitha spp.and Fungia spp. Cytological analysis and histological sections reveal identical cell death mechanisms as shown in Caribbean YBD coral specimens. Inoculation experiments of Indo-Pacific bacterial isolates under ambient temperatures in aquaria cause the induction of YB lesions onto Montastraea spp. in vitro. This recent research indicates that YBD continues to be in an infectious stage in the Caribbean and has been found to cause infection in Pacific coral genera. 7-6 Coral Health And Disease Assessment In The U.S. Pacific Trerritories And Affiliated States Bernardo VARGAS-ANGEL* 1 , Benjamin WHEELER 2 , Jean KENYON 1 , James MARAGOS 3 , Bonnie DEJOSEPH 1 1 Coral Reef Ecosystem Division, NOAA Pacific Islands Fisheries Science Center, Honolulu, HI, 2 Department of Oceanography, University of Hawaii, Honolulu, HI, 3 Remote Islands National Wildlife Refuge Complex, USFWS, Honolulu, HI In 2006 and 2007, quantitative coral disease assessments were conducted at 40 different coral islands, banks, and atolls (Johnston, Palmyra, and Wake Atolls, Howland, Baker, and Jarvis Islands, Kingman Reef, the Main Hawaiian Islands, the Northwestern Hawaiian Islands, Guam, and the Commonwealth of the Northern Mariana Islands), spanning over 3500 km and nearly a 20º latitudinal gradient. Distribution and prevalence were determined from 25 m belt transects at 316 sites, totaling an area of over 90,000 m2 of reef habitat. Ten broad disease categories were recognized, affecting 27 different anthozoan genera; prevalence was computed based on the estimated total number of coral colonies per survey area. The most geographically and taxonomically widespread disease was the skeletal growth anomalies, detected at nearly 60% islands/atolls and on 8 different anthozoan genera. In contrast, the most prevalent disease was the acute tissue loss, aka white syndrome, which exhibited a diverse range of host genera, including Acropora, Montipora, Pocillopora, Goniastrea, and Platygyra. Band diseases were rare, with only two cases enumerated for all the regions on Porites and Coscinaraea. The overall abundance of coral diseases in the US Pacific is low. However, patterns of prevalence vary among coral genera and indicate that only a few taxa are disproportionately affected by disease, namely the Acroporidae and Poritidae. Of potential concern is the white syndrome, which results in severe and rapid tissue loss, particularly on the tabular Acropora cytherea at Johnston Atoll and French Frigate Shoals. Oral Mini-Symposium 7: Diseases on Coral Reefs 7-7 Guam Reefs Show A Link Between The Dominant Genus Porites And Disease Prevalence Roxanna MYERS* 1 , Laurie RAYMUNDO 1 1 Marine Laboratory, University of Guam, Mangilao, Guam Coral diseases are considered to be a major cause, and often a result, of the recent worldwide decline of coral reef health and productivity. Relative to the Caribbean little is known about the impacts of coral diseases on Indo-Pacific reefs which are more widespread with greater diversity and are often more impacted by dense human coastal populations. Therefore, understanding the impact of coral diseases on Guam reefs was considered an important management issue for local scientists. Initial surveys of 12 Guam reefs conducted in 2006-07 revealed mean disease prevalence as highly variable, both within and between sites possessing a weak relationship with live hard coral cover (R2 = 0.01; p>0.05). Coral composition consisted of 13 major families and total disease prevalence ranged from a low of 2% (Pago Bay) to a high of 38% (Cocos Lagoon). Four sites were selected for long-term monitoring of disease prevalence, changes in benthic composition and temperature. Results from the first year of monitoring on Luminao Reef suggest highest disease prevalence corresponding to the period of warmest temperatures (30.1 + 1.0 ºC), with prevalence increasing from 6% to 30% in one year. Guam reefs were taxonomically diverse, but dominated by the genus Porites. They displayed a strong link between total disease prevalence and generic abundance per family (R2=0.89; p

7-9 Coral Disease At Palmyra Atoll in The Remote Central Pacific: Patterns Of Distribution And Histological Characterization Gareth WILLIAMS* 1 , Greta AEBY 2 , Thierry WORK 3 , Simon DAVY 1 1 Victoria University of Wellington, Wellington, New Zealand, 2 Hawaii Institute of Marine Biology, Kaneohe, HI, 3 US Geological Survey, Kaneohe, HI Coral diseases are an ever increasing threat to coral reefs. This is clearly a concern for conservation and management of these systems and their reef associated organisms. This baseline survey was aimed at quantifying, in detail, the relationship between coral disease occurrence, environmental variables and coral community structure. Work was conducted over six weeks at the Palmyra Atoll National Wildlife Refuge, Central Pacific, during June to July 2007. Fifty-eight belt transects were haphazardly placed at 11 key sites (5 backreef and 6 forereef) established for long term monitoring around the atoll. Environmental variables measured were temperature, salinity, turbidity and chlorophyll a concentration. Sedimentation levels were also measured for all back reef sites. Growth anomalies were recorded on four coral genera (Astreopora, Montipora, Fungia and Acropora). In addition, tissue loss was seen on colonies of encrusting Montipora sp. These diseases were restricted to the backreef sites and occurred with an overall prevalence of 0.39 %, with prevalence at individual sites ranging from 0.2 – 1.0 %. This presentation will discuss how prevalence of coral disease relates to the environmental variables and coral community structure using an array of multivariate statistical techniques. Histological characterisation of the Astreopora growth anomalies will also be presented because this type of characterization is crucial to advancing our understanding of how diseases affect coral at a cellular level. Palmyra Atoll represents a location where the prevalence of coral disease and the impacts of environmental variables on this prevalence can be monitored in circumstances where more recent major anthropogenic impact has been greatly reduced. Moreover, knowledge of coral disease at this important wildlife refuge will aid its future monitoring and management. 7-10 Effects Of Quick And Slow Diseases At Acropora Cytherea in Kerama Islands. Akiyuki IRIKAWA* 1 1 Department of Research, Association for Kerama coral Reef Conservation, Naha- Okinawa prefecture, Japan In order to estimate effects of bleaching, Acanthaster planci, and diseases in a population of the reef-building coral Acropora cytherea, decadal monitoring researches have been conducted. The most severe impacts in the A. cytherea population are progressive diseases. Skeletal anomalies (SAs) in A.cytherea develop mainly as white masses. On the surface of SAs, orderly skeletal structure and alignment of polyps became lost, and swelling SAs covered normal area like an avalanche. Negative aspects of SAs are lower potential in productivity and lack of fecundity. Although linear annual growth were 1.2~1.4cm/yr, multiple SAs became fused with neighboring ones. SA tended to start to die over 10cm diameter. If A.cytherea colonies keep usual growth rate, the impact by Sas are acceptable. White syndrome (W.S.D.) arised at 2003, and became widespread at 2004. Approximately 70% colonies of A.cytherea have been killed by W.S.D for recent 3 years. By contrast with SAs, W.S.D have severe impact in a population of A.cytherea. On the lesioned part appearing white band, coral tissues are broken off. White band spread at the rate of up to 20cm centimeters per a month. If W.S.D. does not blow over, A population of A.cytherea in Kerama Islands will be crushed within 10 years by interaction of bleaching, Acanthaster, and disease impacts. Oral Mini-Symposium 7: Diseases on Coral Reefs 7-11 Prevalence And Potential Origin Of The White Pox Disease Pathogen in The Florida Keys, Usa Kathryn SUTHERLAND* 1 , James PORTER 2 , Jeffrey TURNER 2,3 , Brian THOMAS 1 , Erin LOONEY 4 , Trevor LUNA 1 , Victoria WATSON 1 , Erin LIPP 4 1 Department of Biology, Rollins College, Winter Park, FL, 2 School of Ecology, University of Georgia, Athens, GA, 3 Department of Environmental Health Science, University of Georgia, Athens, 4 Department of Environmental Health Science, University of Georgia, Athens, GA Serratia marcescens is a causal agent of the coral disease, commonly known as white pox and etiologically known as acroporid serratiosis, that affects the Caribbean elkhorn coral Acropora palmata. The purpose of this study is to elucidate the prevalence and the source of the bacterium in the marine environment. Nearshore marine and reef environments in the Florida Keys and raw sewage were screened for the presence of the bacterium. S. marcescens were cultured and identified from environmental samples using a three-step method: culture on MacConkey Sorbitol agar followed by culture on DNase with Toluidine Blue agar followed by Serratia-specific PCR. PCR products from a sub-sample of confirmed isolates were sequenced to verify identity. Restriction endonuclease digestion (SpeI) followed by pulsed-field gel electrophoresis (PFGE) was used to determine genetic similarity among and between strains and potential source areas. A total of 383 S. marcescens were isolated from the surface mucopolysaccharide layers of the scleractinian corals Siderastrea siderea and Solenastrea bournoni, the corallivorous snail Coralliophilia abbreviata, seabird guano, beach water, canal water, and sewage. The majority of S. marcescens (72%) were obtained from sewage and contaminated nearshore sources. A total of 118 distinct PFGE patterns were identified, indicating that S. marcescens is genetically diverse in environments of the Florida Keys. Eleven groups (strains) contained two or more identical isolates, and one of these strains included isolates collected from sewage, C. abbreviata, S. siderea, and S. bournoni. This strain, isolated from both reef and sewage sources, establishes a definitive connection between human sewage and the reef ecosystem. 7-12 Epizootiology Of montipora white Syndrome in Kaneohe Bay, Oahu, Hawaii Greta AEBY* 1 , Megan ROSS 2 , Thierry WORK 3 , Teresa LEWIS 1 1 Hawaii Institute of Marine Biology, Kaneohe, HI, 2 University of Hawaii, Honolulu, HI, 3 USGS, Natl Wildlife Health Center, Honolulu, HI Coral disease is emerging as a problem in the Indo-Pacific yet little is known about the ecology of these diseases or factors that may be affecting disease levels. Montipora white syndrome (MWS) is a coral disease resulting in tissue loss that was identified in Kaneohe Bay, Oahu, Hawaii in 2004. Kaneohe Bay has a north-south gradient in anthropogenic stressors and so provided a model system to examine the relationship between proximity to potential stressors and disease prevalence. The objectives of this study were to document the distribution and abundance of Montipora white syndrome on reefs throughout Kaneohe Bay, examine the relationship between disease prevalence and environmental stressors and determine the ultimate damage to coral colonies from this disease. Montipora white syndrome was found in all regions of Kaneohe Bay but prevalence was highest in south Kaneohe Bay, the region most subject to terrestrial run-off. MWS was present on corals throughout the year with no significant difference in disease prevalence in Fall vs. Spring. Fifty-four out of 57 tagged coral colonies infected with MWS experienced progressive tissue loss ranging from 1% of the colony to complete mortality (avg. loss=36.7%) within one year. Average rate of tissue loss was 3.1% per month with one third of the colonies losing 90% or more of their tissues resulting in partial to complete colony collapse within one year. MWS was found to stop and re-start on individual colonies suggesting there are intrinsic and/or extrinsic factors controlling its progression. We also discovered differential susceptibility to MWS between two color morphs of Montipora capitata. 48

7-9<br />

Coral Disease At Palmyra Atoll in The Remote Central Pacific: Patterns Of<br />

Distribution And Histological Characterization<br />

Gareth WILLIAMS* 1 , Greta AEBY 2 , Thierry WORK 3 , Simon DAVY 1<br />

1 Victoria <strong>University</strong> of Wellington, Wellington, New Zealand, 2 Hawaii Institute of<br />

Marine Biology, Kaneohe, HI, 3 US Geological Survey, Kaneohe, HI<br />

Coral diseases are an ever increasing threat to coral reefs. This is clearly a concern for<br />

conservation and management of these systems and their reef associated organisms. This<br />

baseline survey was aimed at quantifying, in detail, the relationship between coral disease<br />

occurrence, environmental variables and coral community structure. Work was conducted<br />

over six weeks at the Palmyra Atoll National Wildlife Refuge, Central Pacific, during<br />

June to July 2007. Fifty-eight belt transects were haphazardly placed at 11 key sites (5<br />

backreef and 6 forereef) established for long term monitoring around the atoll.<br />

Environmental variables measured were temperature, salinity, turbidity and chlorophyll a<br />

concentration. Sedimentation levels were also measured for all back reef sites. Growth<br />

anomalies were recorded on four coral genera (Astreopora, Montipora, Fungia and<br />

Acropora). In addition, tissue loss was seen on colonies of encrusting Montipora sp.<br />

These diseases were restricted to the backreef sites and occurred with an overall<br />

prevalence of 0.39 %, with prevalence at individual sites ranging from 0.2 – 1.0 %. This<br />

presentation will discuss how prevalence of coral disease relates to the environmental<br />

variables and coral community structure using an array of multivariate statistical<br />

techniques. Histological characterisation of the Astreopora growth anomalies will also be<br />

presented because this type of characterization is crucial to advancing our understanding<br />

of how diseases affect coral at a cellular level. Palmyra Atoll represents a location where<br />

the prevalence of coral disease and the impacts of environmental variables on this<br />

prevalence can be monitored in circumstances where more recent major anthropogenic<br />

impact has been greatly reduced. Moreover, knowledge of coral disease at this important<br />

wildlife refuge will aid its future monitoring and management.<br />

7-10<br />

Effects Of Quick And Slow Diseases At Acropora Cytherea in Kerama Islands.<br />

Akiyuki IRIKAWA* 1<br />

1 Department of Research, Association for Kerama coral Reef Conservation, Naha-<br />

Okinawa prefecture, Japan<br />

In order to estimate effects of bleaching, Acanthaster planci, and diseases in a population<br />

of the reef-building coral Acropora cytherea, decadal monitoring researches have been<br />

conducted. The most severe impacts in the A. cytherea population are progressive<br />

diseases.<br />

Skeletal anomalies (SAs) in A.cytherea develop mainly as white masses. On the surface<br />

of SAs, orderly skeletal structure and alignment of polyps became lost, and swelling SAs<br />

covered normal area like an avalanche. Negative aspects of SAs are lower potential in<br />

productivity and lack of fecundity. Although linear annual growth were 1.2~1.4cm/yr,<br />

multiple SAs became fused with neighboring ones. SA tended to start to die over 10cm<br />

diameter. If A.cytherea colonies keep usual growth rate, the impact by Sas are acceptable.<br />

White syndrome (W.S.D.) arised at 2003, and became widespread at 2004.<br />

Approximately 70% colonies of A.cytherea have been killed by W.S.D for recent 3 years.<br />

By contrast with SAs, W.S.D have severe impact in a population of A.cytherea. On the<br />

lesioned part appearing white band, coral tissues are broken off. White band spread at the<br />

rate of up to 20cm centimeters per a month.<br />

If W.S.D. does not blow over, A population of A.cytherea in Kerama Islands will be<br />

crushed within 10 years by interaction of bleaching, Acanthaster, and disease impacts.<br />

Oral Mini-Symposium 7: Diseases on Coral Reefs<br />

7-11<br />

Prevalence And Potential Origin Of The White Pox Disease Pathogen in The Florida<br />

Keys, Usa<br />

Kathryn SUTHERLAND* 1 , James PORTER 2 , Jeffrey TURNER 2,3 , Brian THOMAS 1 , Erin<br />

LOONEY 4 , Trevor LUNA 1 , Victoria WATSON 1 , Erin LIPP 4<br />

1 Department of Biology, Rollins College, Winter Park, FL, 2 School of Ecology, <strong>University</strong> of<br />

Georgia, Athens, GA, 3 Department of Environmental Health Science, <strong>University</strong> of Georgia,<br />

Athens, 4 Department of Environmental Health Science, <strong>University</strong> of Georgia, Athens, GA<br />

Serratia marcescens is a causal agent of the coral disease, commonly known as white pox and<br />

etiologically known as acroporid serratiosis, that affects the Caribbean elkhorn coral Acropora<br />

palmata. The purpose of this study is to elucidate the prevalence and the source of the<br />

bacterium in the marine environment. Nearshore marine and reef environments in the Florida<br />

Keys and raw sewage were screened for the presence of the bacterium. S. marcescens were<br />

cultured and identified from environmental samples using a three-step method: culture on<br />

MacConkey Sorbitol agar followed by culture on DNase with Toluidine Blue agar followed by<br />

Serratia-specific PCR. PCR products from a sub-sample of confirmed isolates were sequenced<br />

to verify identity. Restriction endonuclease digestion (SpeI) followed by pulsed-field gel<br />

electrophoresis (PFGE) was used to determine genetic similarity among and between strains<br />

and potential source areas. A total of 383 S. marcescens were isolated from the surface<br />

mucopolysaccharide layers of the scleractinian corals Siderastrea siderea and Solenastrea<br />

bournoni, the corallivorous snail Coralliophilia abbreviata, seabird guano, beach water, canal<br />

water, and sewage. The majority of S. marcescens (72%) were obtained from sewage and<br />

contaminated nearshore sources. A total of 118 distinct PFGE patterns were identified,<br />

indicating that S. marcescens is genetically diverse in environments of the Florida Keys.<br />

Eleven groups (strains) contained two or more identical isolates, and one of these strains<br />

included isolates collected from sewage, C. abbreviata, S. siderea, and S. bournoni. This strain,<br />

isolated from both reef and sewage sources, establishes a definitive connection between human<br />

sewage and the reef ecosystem.<br />

7-12<br />

Epizootiology Of montipora white Syndrome in Kaneohe Bay, Oahu, Hawaii<br />

Greta AEBY* 1 , Megan ROSS 2 , Thierry WORK 3 , Teresa LEWIS 1<br />

1 Hawaii Institute of Marine Biology, Kaneohe, HI, 2 <strong>University</strong> of Hawaii, Honolulu, HI,<br />

3 USGS, Natl Wildlife Health Center, Honolulu, HI<br />

Coral disease is emerging as a problem in the Indo-Pacific yet little is known about the ecology<br />

of these diseases or factors that may be affecting disease levels. Montipora white syndrome<br />

(MWS) is a coral disease resulting in tissue loss that was identified in Kaneohe Bay, Oahu,<br />

Hawaii in 2004. Kaneohe Bay has a north-south gradient in anthropogenic stressors and so<br />

provided a model system to examine the relationship between proximity to potential stressors<br />

and disease prevalence. The objectives of this study were to document the distribution and<br />

abundance of Montipora white syndrome on reefs throughout Kaneohe Bay, examine the<br />

relationship between disease prevalence and environmental stressors and determine the ultimate<br />

damage to coral colonies from this disease. Montipora white syndrome was found in all regions<br />

of Kaneohe Bay but prevalence was highest in south Kaneohe Bay, the region most subject to<br />

terrestrial run-off. MWS was present on corals throughout the year with no significant<br />

difference in disease prevalence in Fall vs. Spring. Fifty-four out of 57 tagged coral colonies<br />

infected with MWS experienced progressive tissue loss ranging from 1% of the colony to<br />

complete mortality (avg. loss=36.7%) within one year. Average rate of tissue loss was 3.1%<br />

per month with one third of the colonies losing 90% or more of their tissues resulting in partial<br />

to complete colony collapse within one year. MWS was found to stop and re-start on individual<br />

colonies suggesting there are intrinsic and/or extrinsic factors controlling its progression. We<br />

also discovered differential susceptibility to MWS between two color morphs of Montipora<br />

capitata.<br />

48

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