|
TEMPERATURE AND UV STRESS INTERACT TO CHANGE
THE PIGMENT COMPOSITION OF CORAL ZOOXANTHELLAE
By Maria Bynagle and Emily Peterson under the advisement of Suzanne
Strom
Shannon Point Marine Center, Western Washington University, Bellingham,
WA 98225-9181
INTRODUCTION
Coral bleaching is an increasingly widespread
event and a serious environmental and economic problem for many tropical
countries. A major world-wide bleaching event was observed during the 1997-1998
ENSO. In general, coral bleaching is strongly associated with elevated
seawater temperatures and increased exposure to UV radiation. Our goal
in this project is to understand the pigmentation changes associated with
temperature and UV stress in the coral Montastraea faveolata.
Specifically,
-
Did bleaching occur? Was bleaching induced by temperature stress,
UV stress, or both?
-
Are observed stress induced changes in coral pigmentation caused by expulsion
of zooxanthellae or by changes in the pigment content of zooxanthellae
retained in the host?
-
Does the pigment content of expelled zooxanthellae differ from the pigment
content of zooxanthellae retained in the host?
-
Is there a change in zooxanthellar pigment composition as the algae respond
to temperature and UV stress?
Ultimately, we will relate these pigmentation changes
to 1) changes in the photosynthetic capability of the coral zooxanthellae;
and 2) changes in the whole coral optical spectra.
METHODS
-
Plugs (2.1 cm dia.) of the boulder coral Montastraea faveolata were collected
from three North Perry Reef colonies (Lee Stocking Island, Bahamas) at
a depth of 15+1 m.
-
Two experiments were conducted, one at ambient temperature and one at elevated
temperature. The temperature was kept constant using a temperature-controlled
water circulation system.
-
We used natural density screen and mylar to simulate three different light
environments.
|
Simulated Environment
|
UVB (% surface irradiance)
|
PAR (% surface irradiance)
|
|
Reef
|
1.3
|
24.2
|
|
Reef + UV
|
16.9
|
30.0
|
|
Enhanced
|
54.4
|
57.8
|
For comparison ,% Surface Irradiance at N. Perry
Reef (16m): 24.1% PAR, 0.58% UVB
-
Three coral plugs from each treatment were sampled every 24 hours. The
water from each holding dish was collected for the expelled zooxanthellae.
The tissue was removed from the skeleton of the coral using an Interplaq
water pik for the zooxanthellae retained in the host.
-
After repeated centrifugation, the final resuspension of coral zooxanthellae
was filtered through 30 mm Nitex mesh. The zooxanthellar suspension was
vacuum filtered onto GF/C filters, wrapped in foil and placed in liquid
nitrogen for later analysis by HPLC.
-
Filters were ground using 100% acetone. An internal standard, canthaxanthin,
was added to the samples after they were ground and centrifuged.
-
HPLC pigment separation was by a modification of the method of Mantoura
and Llewellyn (1983). A methanol-acetone gradient was used on a C-18 reverse
phase column with 5 mm particle size, flow rate 1 mL/min.
-
The pigments present in the eluent were detected and quantified using fluorescence
and absorbance detection (Mantoura and Repeta, 1997).
RESULTS
Bleaching Response
-
Bleaching was evident at both temperatures in enhanced light treatments.
-
No bleaching occurred in response to temperature stress alone (as shown
by ambient temp exp).
-
Temperature and UV stress combined to cause a more severe bleaching response
(as shown by differing reef + UV response in the two temp conditions).
Mechanism of Bleaching
Ambient Temperature
-
Bleaching, which occurred in the enhanced light treatment, was a result
of zooxanthellar expulsion.
-
Pigment/cm² decreased (Figure
1)
-
Pigment/cell remained constant (Figure
2)
-
Cell density decreased (Figure 3)
Elevated Temperature
-
Enhanced light treatment showed bleaching as a result of both zooxanthellar
expulsion and loss of pigment within retained zooxanthellae.
-
Pigment/cm² decreased (Figure
1)
-
Pigment/cell decreased (Figure 2)
-
Cell density decreased (Figure 3)
-
Reef + UV treatment exhibited bleaching due only to loss of pigment in
retained zooxanthellae.
-
Pigment/cm² decreased (Figure
1)
-
Pigment/cell decreased (Figure 2)
-
Cell density remained constant (Figure
3)
Pigment content in expelled vs. retained zooxanthellae
-
In all cases, expelled zooxanthellae have far more unknown xanthophyll
than retained zooxanthellae (Figures
4 and 5).
-
Without temperature stress, expelled and retained zooxanthellae had similar
chlorophyll a content (Figure
6 ).
-
With temperature stress, expelled zooxanthellae had less chlorophyll a
than retained zooxanthellae (Figure
7).
Changes in Pigment Composition
-
Stress caused an increase in photoprotective pigments relative to the total
pigment content (Figures 8
and 9 and Figures 10
and 11).
-
Expelled zooxanthellae showed a much larger increase in the photoprotective/total
pigment ratio over time compared to the retained zooxanthellae (Figures
10 and 11).
-
The continuous increase in the pigment ratio for expelled zooxanthellae
shows that they were experiencing stress within the animal prior to their
expulsion (Figures 10 and
11).
|
Photoprotective Pigments
|
Photosynthetic Pigments
|
|
dinoxanthin
|
chlorophylls a & c
|
|
diadinoxanthin
|
peridinin
|
|
unknown xanthophylls
|
B-carotene
|
Conclusions
-
Exposure to enhanced light intensities caused bleaching; temperature stress
led to bleaching at lower light intensities.
-
Different environmental stresses (e.g. UV, temperature) seem to cause bleaching
through different pigment loss mechanisms.
-
"Unknown xanthophylls" appeared to be produced in response to stress, especially
in expelled zooxanthellae.
ACKNOWLEDGEMENTS
The authors would like to thank : PIs Gisele Muller-Parker,
Suzanne Strom, and Jack Hardy, NSF grand C-RUI DBI 97-11075, Shannon Point
Marine Center Staff, Kelley Bright, Scientific Technical Services at WWU,
Caribbean Marine Research Center, Erin Macri, Adrienne Miller, Trevor Rivers,
Teresa Stelly, and Carl Schmidt.
| STUDENT PROJECTS
|
|
Shannon
Point
Marine
Center |