Thermal Adaptation - Coral Symbiosis
The Great Barrier Reef (GBR) is an important environmental
and economic asset to North Queensland. As a result of warming ocean
temperatures, six coral bleaching events have occurred in the GBR since 1980
(Berkelmans 2001). Progression of coral bleaching in this ecosystem will affect
countless marine species with negative economic impacts to tourism (Strasser et
al 1999). This blog post will discuss the potential of thermally-resilient
symbiotic algae in order to reduce coral bleaching in the GBR.
Coral is the foundation of the GBR, providing shelter,
feeding and breeding grounds for many marine organisms. However due to increasing
ocean temperatures, coral bleaching is occurring (Fig.1). A 2001 JCU study found that upper
thermal limits of coral in the GBR were only 2-4°C higher
than average summer temperature, and within 1°C of daily
average temperatures during summer periods (Berkelmans 2001). The white colour
is caused by the death of zooxanthellae (Symbiodinium),
occurrent within the gastrodermic cells of the coral as a symbiotic
relationship (Ban & Graham 2012). The physiology of bleaching is not fully
understood but involves the production of oxygen radicals, which are highly
corrosive and damage chloroplasts (Berkelmans 2001).
(Fig. 1 - Coral Bleaching events between 1994 and 1998 - dark spots represent reports of bleached coral, light spots represent reports of healthy coral)
(Berkelmans 2001)
(Berkelmans 2001)
Thermal adaptation of coral could be achieved by
transplanting heat-resilient zooxanthellae. A 2004 study found that in Guam,
corals of the genus Pocillopora
associate with both Symbiodinium C
and thermally resilient species ‘D’ (Rowan 2004). In a 2006 research project, coral
nubbins containing Symbiodinium D
were transplanted to Magnetic Island, North Keppel Island and Davies Reef.
Magnetic and North Keppel islands experienced significant increases in
zooxanthellae density and reductions in bleaching/death of coral. Corals
exposed to 32°C in the Keppel
control had no zooxanthellae, with more than 60% of corals bleached and the
rest dead. After treatment, over 50% of corals in this area at 32°C were surviving with reduced bleaching and
significant reduction in mortality (Fig. 2) (Berkelmans & Van Oppen 2006).
(Fig. 2 - Zooxanthellae density in corals before and after transplanting at North Keppel Island sites (bar graph), pie graphs represent coral status; (grey) healthy, (white), bleached and (black) dead) (Berkelmans & Van Oppen 2006)
Coral bleaching is a significant problem for the GBR. In
1998, 87% of 2900 reef systems were affected by at least moderate bleaching
(Berkelmans 2001). Coral transplanting has increased zooxanthellae density, and
reduced coral bleaching/mortality but only in 30 - 32°C conditions. The increased tolerance of Keppel corals
with Symbiodinium D is only about 1 -
1.5°C (Berkelmans & Van Oppen 2006). Transplanting
of corals with Symbiodinium D has
resulted in increased thermal tolerance of corals, however application of this
research as a thermal adaptation would only be effective temporarily as
temperatures continue to rise.
References:
Ban, S.S. Graham, N.A.J. 2012, ‘Relationships between
temperature, bleaching and white syndrome on the Great Barrier Reef’, Coral Reefs, Vol. 32, pages 1–12
Berkelmans, R. 2001, ‘Bleaching, upper thermal limits and temperature adaptation in reef corals’, PhD thesis, James Cook University
Berkelmans, R. Van Oppen, M.J.H. 2006, ‘The role of zooxanthellae in the thermal tolerance of corals: a ‘nugget of hope’ for coral reefs in an era of climate change’, Proceedings of The Royal Society of Biology, Volume 273, pages 2305-2312.
Rowan, R. 2004, ‘Thermal adaptation in reef coral symbionts’, Nature, Vol. 430, page 742
Strasser, R.J. Tsimilli-Michael, M. Pecheux, M. 1999, ‘Perpetual adaptation in
a perpetually changing environment as a survival strategy of plants: a case
study in foraminifers concerning coral reef bleaching’, Photosynthetica, Vol. 37, pages 71-85
Figures:
Figure 1: Berkelmans, R. 2001, ‘Bleaching, upper thermal limits and temperature adaptation in reef corals’, "Records of bleaching on the reef from 1994 to 1998", PhD thesis, James Cook University
Figure 2: Berkelmans, R. Van Oppen, M.J.H. 2006, ‘The role of zooxanthellae in the thermal tolerance of corals: a ‘nugget of hope’ for coral reefs in an era of climate change’, "Zooxanthella densityGs.e. (bars) and coral condition (pies) of coral nubbins", Proceedings of The Royal Society of Biology, Volume 273, page 2311
Fascinating. Does the six bleaching events mentioned include the latest one that’s just been reported in the media? Are there any other symbioses that could potentially be exploited to minimise bleaching?
ReplyDeleteNo, there would definitely be more bleaching events since that paper was published in 2001 unfortunately
DeleteTheres other symbiotic relationships occuring in the reef (anenome and clown fish) but none really that would benefit zooxanthellae or the coral as far as i know
No, there would definitely be more bleaching events since that paper was published in 2001 unfortunately
DeleteTheres other symbiotic relationships occuring in the reef (anenome and clown fish) but none really that would benefit zooxanthellae or the coral as far as i know