11th ICRS Abstract book - Nova Southeastern University
11th ICRS Abstract book - Nova Southeastern University
11th ICRS Abstract book - Nova Southeastern University
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7-1<br />
Patterns of Coral Diseases in the Florida Keys from 1998 – 2005<br />
Deborah SANTAVY* 1 , Susan YEE 1 , Mace BARRON 1<br />
1 Gulf Ecology Division, US EPA, NHEERL, Gulf Breeze, FL<br />
Diseases have been identified as a major threat to reef-building corals causing morbidity<br />
and mortality. Increased mortality has lead to degradation, especially those reefs<br />
dominated by several susceptible species. Increased morbidity has reduced the health of<br />
reef-building corals making them more vulnerable to other environmental stressors.<br />
Reported incidence, prevalence, and distribution of coral diseases have been greatest<br />
from the tropical Western Atlantic, with emergent coral diseases, such as aspergillosis<br />
and serratiosis originating from terrestrial sources. Epizootiological studies assessed the<br />
prevalence of dominant coral diseases in the Florida Keys reef tract from 1998-2005,<br />
from the Dry Tortugas to the Upper Keys. Annual assessments were repeated at<br />
permanent sites in mid-summer throughout the area. Data were adjusted so coral<br />
community composition, specifically the absence of susceptible species, did not bias the<br />
results. Canonical correspondence analyses revealed coral diseases patterns related to<br />
spatial and temporal parameters. Reef depth was the most discriminating parameter for<br />
all coral diseases surveyed. White plague and white-band disease had the highest<br />
prevalence on deeper reefs, whereas black-band disease was most prevalent on mid-depth<br />
reefs, and red-band disease and white pox were most prevalent on shallow reefs. Whiteband<br />
disease had the highest prevalence in the early years, whereas dark-spots disease<br />
had increased incidence in the later years of the study. Dark-spots and yellow-blotch<br />
diseases were more common in the Dry Tortugas, whereas black-band disease had the<br />
highest prevalence in the Middle Keys. One of the first steps in identifying and managing<br />
health threats of reefs is to establish disease prevalence and incidence to understand<br />
patterns and associate them with other variables to determine causative factors. In<br />
tropical marine systems prevention or control of coral disease can assist in precluding the<br />
collapse of important ecological functions and ecosystem services.<br />
7-2<br />
The Role Of Diseases in Coral Community Structure Shifts in Mexican Caribbean<br />
Reefs<br />
Eric JORDÁN-DAHLGREN* 1 , Rosa RODRÍGUEZ-MARTÍNEZ 2 , Adan Guillermo<br />
JORDÁN-GARZA 3 , David M. BAKER 4 , Jason ANDRAS 5 , Leonardo VAZQUEZ-<br />
VERA 6<br />
1 ICMyL, UAPM, Universidad Nacional A. de México, Puerto Morelos, Mexico, 2 ICMyL,<br />
UAPM, Universidad nacional A. de México, Puerto Morelos, Mexico, 3 ICMYL, UAPM,<br />
UNiversidad Nacional A. de México, Puerto Morelos, Mexico, 4 Ecology and<br />
evolutionary Biology, Cornell <strong>University</strong>, Ithaca, NY, 5 Ecology and Evolutionary<br />
biology, Cornell <strong>University</strong>, Ithaca, NY, 6 ICMyL,UAPM, Universidad Nacional A. de<br />
México, Puerto Morelos, Mexico<br />
Montastraea annularis, M. faveolata and M. franksi, the major local coral reef builders<br />
after the demise of Acroporids in the Mexican Caribbean, has decreased more than half in<br />
a twenty years span; presumably due to diseases. Recent data (2005-2007) from highly<br />
replicated permanent sites spread over a 200km reef tract shows relatively large rates of<br />
whole colony and partial mortality for these species, both within and between sampling<br />
sites. Yellow Blotch syndrome appears to be the major cause of the observed mortality<br />
patterns, although other disease signs also play a role. Species of Acropora, Diploria and<br />
Colpophyllia natans, the other potentially important reef builders are also being severely<br />
affected by other diseases. In contrast Agaricia agaricites, Porites astreoides and<br />
Siderastrea siderea while not being immune to coral diseases show a much higher<br />
resistance and mortality rates are comparably low; becoming the dominant components in<br />
reefs down to 15m deep. Although variable among sites, comparisons of species size<br />
structures indicates that local shifts in dominant species appears to be related to higher<br />
survival rates, rather than to increased recruitment rates. Analyzing linkages of the<br />
observed patterns with site relative degree of local development, protected and nonprotected<br />
status and local thermal anomalies shows mixed trends. These findings suggest<br />
that global and regional drivers of environmental deterioration may have a stronger<br />
influence than local ones in the study area.<br />
Oral Mini-Symposium 7: Diseases on Coral Reefs<br />
7-3<br />
Recent Changes To Montastraea Annularis And M. Faveolata Populations In<br />
Southwestern Puerto Rico And Associated Islands From Disease And Bleaching<br />
Andrew BRUCKNER* 1 , Ron HILL 2<br />
1 NOAA Coral Reef Conservation Program, NOAA, Silver Spring, MD, 2 Fisheries, NOAA,<br />
Galveston, TX<br />
Over the last decade, reefs off southwest Puerto Rico and the associated islands have<br />
experienced losses in live coral cover in excess of 50%, primarily due to the decline of M.<br />
annularis and M. faveolata. These species were formerly the largest and most abundant corals<br />
remaining on these reefs. Outbreaks of coral disease, especially white plague and yellow band<br />
disease, affected over 50% of the colonies in some sites during the late 1990s; disease<br />
prevalence declined between 2002-2004 and then increased immediately following a 2005 mass<br />
bleaching event. These diseases have caused unprecedented rates of mortality, with cumulative<br />
losses exacerbated by bleaching and parrotfish predation. In both species, a lack of recruitment<br />
and only limited recovery through resheeting have been observed, and exposed skeletal surfaces<br />
are being colonized by macroalgae, bioeroding sponges, hydrozoans, and other scleractinian<br />
coral recruits (primarily Porites and Agaricia). Unlike acroporids, which have the potential for<br />
rapid growth and recovery, M. annularis and M. faveolata are unlikely to recover in our<br />
lifetimes and are being replaced by shorter-lived brooding species and other massive and plating<br />
species with faster growth and higher recruitment rates. The impacts of these shifts on coral<br />
community structure and reef fisheries are unknown. Approaches undertaken to recover<br />
acroporids, such as propagation through fragmentation and grow-out of sexual recruits, are less<br />
likely to work for M. annularis (complex) - species with slow rates of growth and limited<br />
recruitment. To avoid a catastrophic and permanent shift in coral community composition,<br />
research needs to be directed towards an improved understanding of the causes and impacts of<br />
diseases and bleaching, and possible control mechanisms. Managers and policy makers must<br />
take steps to mitigate environmental and anthropogenic stressors that increase the spread and<br />
severity of disease.<br />
7-4<br />
The Future Of Coral Reefs in The Us Virgin Islands: Why acropora Palmata Is More<br />
Likely To Recover Than montastraea Annularis Complex<br />
Caroline ROGERS* 1 , Erinn MULLER 2 , Tony SPITZACK 1 , Jeff MILLER 3<br />
1 US Geological Survey, St John, Virgin Islands (U.S.), 2 Florida Institute of Technology,<br />
Melbourne, FL, 3 National Park Service, St John, Virgin Islands (U.S.)<br />
The Caribbean bleaching/disease event that began in the summer of 2005 caused significant<br />
mortality of the two most important reef-building corals in the US Virgin Islands (USVI),<br />
Acropora palmata and Montastraea annularis complex (Macx). These corals characterize<br />
the shallow and mid-depth zones of the islands’s reefs, and their ability to recover will define<br />
the future seascape in the USVI. Research on A. palmata from 2003 to 2007 around St. John<br />
documented disease prevalence ranging from 0 to 52% with high levels of white pox (and undescribed<br />
diseases) and very low levels of white band disease that caused major losses 25-30<br />
years ago. Over 94% of the white pox lesions healed at least partially. Acropora palmata<br />
bleached for the first time in the USVI in 2005. Forty-five percent of 460 colonies from several<br />
sites bleached, and 8% died. Bleached corals had greater disease mortality than unbleached.<br />
Acropora palmata had high genotypic variation, and evidence of limited, recent sexual<br />
recruitment. Survival of fragments ranged from 29 to 60%. Deeper reef zones dominated by<br />
Macx showed greater coral bleaching and mortality (primarily from white plague) following the<br />
record-high seawater temperatures in 2005. Over 98% of the Macx bleached, and ca. 90% of the<br />
disease mortality was seen on Macx. Healing of disease lesions was not observed. Over the<br />
next 50 to 100 years, A. palmata has a greater potential to recover than Macx because of its<br />
higher growth rate, greater ability to colonize new areas through fragmentation, and lower<br />
vulnerability to bleaching and disease. The future of these major reef-building corals and of<br />
USVI reefs will depend also on the connectivity between these reef zones and sources of coral<br />
larvae.<br />
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