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NOAA |
NESDIS |
STAR |
SOCD |
MEB |
Satellite Coral Bleaching Monitoring
The coral reef is a unique and very rich ecosystem which
supports a vast array of animal and plant species. The
fisheries dependent on coral reefs have supported many
cultures for ages. Corals form the structural and
ecological foundation of the reef system. Coral reefs
flourish mainly in the tropical latitudes, extending at
most to 30° north or south of the Equator in only a
few cases. Every coral species, as well as numerous
other reef inhabitants, maintains a special symbiotic
relationship with a microscopic organism (algae) called
zooxanthallae.
These organisms provide their hosts with
oxygen and a portion of the organic compounds they
produce through photosynthesis. When stressed, many
reef inhabitants have been observed to expel their
zooxanthallae en masse. The polyps of the coral are
left bereft of pigmentation and appear nearly
transparent on the animal's white skeleton. This
phenomenon is normally referred to as coral bleaching.
More severe bleaching events have dramatic long-term
effects on the coral. The ability of the coral to feed
itself in the absence of zooxanthallae may
be very important to its survival during and after a
bleaching event. Recovery rates appear to differ, however,
with species, and the time required to attain full
recovery of symbiotic algae may vary from as little as
2 months to as much as one year. When the level of
environmental stress is high and sustained the coral may
die.
The bleaching events reported prior to the 1980s were
generally attributed to localized phenomena such as
major storm events, severe tidal exposures, sedimentation,
rapid salinity changes, pollution, or thermal shock. The
events since 1980 have not been so easily explained.
Numerous laboratory studies have shown a direct
relationship between bleaching and water temperature
stress. Elevated water temperatures have been implicated
in the majority of the major bleaching events of the
1980s and 1990s.
Coral bleaching related to thermal stress has become much
more severe in the last decade. High temperatures
associated with the 1997-98 El Niño
caused bleaching in
much of the world's oceans, with the greatest bleaching in
the Indian and western Pacific Oceans. Heating caused
major bleaching around the Great Barrier Reef and
Northwestern Hawaiian Islands in 2002, and in 2005 we saw
the highest heat stress in the Caribbean region of 20 years
of satellite monitoring. The 1998 and 2005 events have
raised public attention to the plight of coral reefs
(see Mark Trail comic at right).
For more information regarding our ongoing research on coral bleaching,
please contact
coralreefwatch@noaa.gov
United States Coral Reef Task Force
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Last revision: 23 April 2009
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Our Satellite Monitoring
With the capability of providing synoptic views of the global oceans
in near-real-time and the ability to monitor remote reef areas
previously known only to wildlife, satellite remote sensing has
become a key tool for coral reef managers and scientists. As early
as 1997, NOAA's NESDIS began producing near-real-time,
Web-accessible, satellite-derived SST products to monitor conditions
conducive to coral
bleaching from thermal stress around the globe. This activity evolved
into a crucial part of NOAA's Coral Reef Watch (CRW) Program in 2000.
Recently, most of its key products, including SST anomalies, bleaching
HotSpot anomalies, Degree Heating Weeks (DHW), and Tropical Ocean Coral
Bleaching Indices have become "operational" products after
successfully providing early warnings of coral bleaching to the global
coral reef
community as "experimental" products for several years.
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