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11th ICRS Abstract book - Nova Southeastern University

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7-37<br />

Developing An Expert System For Predicting Coral Disease Risk On Indo-Pacific<br />

Reefs<br />

Bette L. WILLIS* 1 , Scott F. HERON 2 , Cathie A. PAGE 3 , William J. SKIRVING 2 , C.<br />

Mark EAKIN 2 , C. Drew HARVELL 4 , Dean M. JACOBSEN 5 , Gregg COLEMAN 6 , Ian<br />

MILLER 6 , Hugh P.A. SWEATMAN 6<br />

1 School of Marine and Tropical Biology and ARC Centre of Excellence for Coral Reef<br />

Studies, James Cook <strong>University</strong>, Townsville, Australia, 2 NOAA Coral Reef Watch,<br />

Silver Spring, MD, 3 School of Marine and Tropical Biology and ARC Centre of<br />

Excellence for Coral Reef Studies, James Cook <strong>University</strong>, Townsville, Queensland,<br />

Australia, 4 Department of Ecology and Evolutionary Biology, Cornell <strong>University</strong>, Ithaca,<br />

NY, 5 College of the Marshall Islands, Majuro, United States Minor Outlying Islands,<br />

6 Australian Institute of Marine Science, Townsville, Queensland, Australia<br />

Coral disease outbreaks represent an emerging risk on Indo-Pacific reefs that is likely to<br />

escalate with ocean warming due to climate change. Building on a recent model that<br />

links the abundance of coral disease with elevated temperature anomalies and percent<br />

cover of coral hosts, we further refine temperature metrics to include both the duration<br />

and magnitude of temperature anomalies and to differentiate between the effects of warm<br />

versus cool seasonal anomalies on disease risk. Using a 9-year data set of disease records<br />

for white syndrome on 48 reefs spanning more than 1000 km along the Great Barrier<br />

Reef, we explore patterns in disease abundance with percent coral cover and with<br />

deviations from both mean summer and mean winter sea surface temperatures. Analysis<br />

showed that each of these factors is necessary but not sufficient to explain patterns in<br />

disease abundance. The addition of winter temperature anomalies to the model improved<br />

its explanatory power. Disease abundance was greatest in summers following mild<br />

winters that deviated by less than 5 °C-weeks from mean winter conditions. We suggest<br />

that cold winters may reduce pathogen loads, and consequently the likelihood of disease<br />

outbreaks in the following summer. It is less clear why warm winters are correlated with<br />

reduced disease abundance, but they may result in enhanced disease resistance of the<br />

coral host. Our results indicate that predicting disease risk on Indo-Pacific reefs is<br />

complex; nevertheless predictions based on satellite-derived sea surface temperatures can<br />

be reasonably accurate, given knowledge of coral cover. With the incorporation of<br />

further factors, such as current speed and host susceptibility, our aim is to provide reef<br />

managers with an expert system for predicting disease risk on coral reefs.<br />

7-38<br />

A Large Semi-Open Aquarium As A Proxy For Natural Coral Reef Ecosytems:<br />

Insights And Implications For The Causes Of Coral Disease<br />

Shelley L. ANTHONY* 1<br />

1 Marine and Tropical Biology, James Cook <strong>University</strong>, Townsville, Australia<br />

Changing water quality parameters of ocean waters have been implicated in the<br />

occurrence of some coral diseases, and are an ongoing concern for the future health of<br />

coral reefs. However, it is difficult and somewhat haphazard to monitor water quality<br />

accurately and continuously in natural reef settings.<br />

The Coral Reef Exhibit (CRE) at Reef HQ Aquarium in Townsville, Australia is the<br />

world’s largest living coral reef aquarium, containing almost 3,000,000 litres of natural<br />

seawater that is open to the atmosphere. The CRE supports thousands of scleractinian and<br />

soft coral colonies, as well as other associated reef species, in a semi-closed system that<br />

simulates a natural reef environment. This system is constantly monitored for<br />

temperature, salinity, pH, alkalinity, dissolved oxygen, turbidity, trace elements, and<br />

inorganic nutrients, among others. Additional and potentially complicating factors in<br />

coral disease observations - such as snail predation - are easily controlled, making it more<br />

efficient to examine the effects of varying conditions on the corals, fish, and other marine<br />

organisms.<br />

Analysis of coral mortality data from 1996-2006 in the CRE system clearly shows that<br />

White Syndrome is the single leading cause of death for acroporids (the most sensitive<br />

group). Extensive water quality records over the same time period were thoroughly<br />

examined and compared to mortality data to look for correlations with White Syndrome<br />

outbreaks. No significant correlations were apparent for any single water quality<br />

parameter, including high temperature. Rather, I suggest that a combination of factors<br />

may create a stressful environment, resulting in White Syndrome occurring after a<br />

prolonged period. Preliminary evidence also indicates that episodes of poor water<br />

circulation are a trigger for tissue sloughing in individual acroporid colonies.<br />

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

7-39<br />

Ecosystem Function And Disease Resistance in Coral Reefs: What Happens When We<br />

Remove Key Players?<br />

Laurie RAYMUNDO* 1 , Aileen MAYPA 2 , Andrew HALFORD 1<br />

1 <strong>University</strong> of Guam, Mangilao, Guam, 2 <strong>University</strong> of Hawaii, Honolulu, HI<br />

The ecological drivers of disease outbreaks are poorly understood. We tested the hypothesis that<br />

intact, trophically-diverse marine ecosystems are less likely to sustain disease outbreaks than<br />

over-fished systems. Marine Protected Areas (MPAs) are a best practice for managing fish<br />

communities, so an additional benefit of this primary tool is a win-win situation for coral reef<br />

conservation. This is challenging to test; few MPAs are consistently well-managed so that<br />

significant increases in fish diversity can occur. We surveyed 7 reefs containing both an MPA<br />

and a fishing ground in the central Philippines for coral disease prevalence and fish taxonomic<br />

distinctness. All MPAs had less disease and taxonomic distinctness on par with, or richer than,<br />

expected. Conversely, fished reefs contained more disease and fish assemblages of higher<br />

variability and lower distinctness. Our findings show that protection from fishing confers<br />

protection from disease outbreaks. At present, this is the only option available for managing<br />

coral diseases.<br />

7-40<br />

Advancing The Global Coral Disease Database<br />

Emily CORCORAN* 1 , Andy BRUCKNER 2 , Nicola BARNARD 3 , Michael STRONG 4 , Craig<br />

MILLS 5<br />

1 One Ocean Programme, UNEP-WCMC, Cambridge, United Kingdom, 2 Coral Reef<br />

Conservation Program, NOAA, Silverspring, MD, 3 ICRAN, Cambridge, United Kingdom,<br />

4 Informatics, UNEP-WCMC, Cambridge, United Kingdom, 5 Spatial Analysis, UNEP-WCMC,<br />

Cambridge, United Kingdom<br />

The Global Coral Disease Database (GCDD) was launched by NOAA and UNEP-WCMC in<br />

2000. Over the last seven years, this partnership has worked to compile and organise published<br />

data on the occurrence of coral disease, benefiting managers, scientists and other stakeholders<br />

through the provision of the first compilation on the global observations of coral diseases. The<br />

database currently contains 7813 data points from 66 countries across the world since 1970,<br />

25% of these data points are observations since 2000.<br />

Whilst excellent advances have been made in developing the GCDD (http://www.unepwcmc.org/GIS/coraldis/),<br />

there exists a need to address the recurrent challenges of quality,<br />

accessibility, and completeness of the data, to ensure that this unique GIS tool meets its fulfil<br />

potential as a critical global repository for coral reef disease information.<br />

A new twelve-month phase of work will be initiated at <strong>ICRS</strong> 11 to improve the relevance and<br />

importance of the database to users through consultation and a comparative analysis of user<br />

needs, information holdings, and data collection. Through partnerships with data collection<br />

programmes, and the establishment of an expert advisory group, the project will raise the profile<br />

and value of the GCDD to stakeholders, build confidence in the holdings, and provide a<br />

mechanism for quality assurance of the data collected. A new visual interface will be<br />

demonstrated which will enhance the visibility and functionality of the GCDD with an<br />

improved look, feel and progression towards a more sophisticated online analysis. Such analysis<br />

would allow ad-hoc spatial querying and analysis, and the manipulation of the coral disease<br />

data alongside key biodiversity datasets, such as the World Database on Protected Areas.<br />

55

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