Coral Growth in Response to Increased Atmospheric CO 2

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Coral Growth in Response to Increased Atmospheric CO 2. Jim Billingsley Biology 881 University of Nebraska, Kearney. Introduction. Overview Coral Structure Seawater Chemistry Affects of CO 2 on Seawater Conclusions. Overview. CO 2 emissions Physiology of marine organisms.  CO 2 - PowerPoint PPT Presentation

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  • Coral Growth in Response to Increased Atmospheric CO2Jim BillingsleyBiology 881University of Nebraska, Kearney

  • IntroductionOverviewCoral StructureSeawater ChemistryAffects of CO2 on SeawaterConclusions

  • OverviewCO2 emissions Physiology of marine organisms.CO2CO32-

  • Overview

    Photosynthesis and calcification problemsSealevel riseFaster growing algaeBoring organisms and storm damage

  • Trends in Atmospheric CO2Mauna Loa, Hawaii and Law Dome, Antarctica(Etheridge et al, 1998); (Keeling and Whorf, 2001)Vostok, Antarctica Ice Core Atmospheric CO2 Record(Petit, et al, 1999)

  • Global Emission of CO2(Marland, Boden and Andres 2001)

  • Coral Structure

    PolypsColonyNematocysts

  • Coral Structure

    AnimalCalcium carbonate skeletonSymbiotic plant

  • Zooxanthellae

    DinoflaggellatePhotosyntheticPigments

  • Seawater ChemistryH2O + CO2 (aq) H2CO3 HCO3- + H+

  • Dissolution of calcium carbonateTemperature, pressure and partial pressure of carbon dioxideCaCO3 + H20 + CO2 Ca2+ + 2HCO3-Higher pressures and cooler temperaturesCorrosive

  • CO2 Emissions and Calcification in the OceansRising atmospheric CO2 Carbonate equilibrium Decrease in alkalinityReduces the CaCO3 saturation Harder for coral reefs to grow1880PresentFuture Double CO2

  • Calculated changes seawater carbonate chemistry(assuming S=35, TA=3.5 meq/L)WaragCO2 aq

  • Observations at the Hawaii Ocean Times Series Station

  • Chemical treatments

  • Effect of CO2 on community calcification

  • Coral Response(Marubini et al., 2001) 200 matm700 matmPorites compressa

  • Effect of a doubling in CO2 (350-700) on calcification, (% decrease)Calcareous macroalgaeAmphiroa foliacea-36 Borowitzka, 1981Porolithon gardineri-16 Agegian, 1985Corallina pilulifera-44 Gao et al., 1993

    CoralsStylophora pistillata -3 Gattuso et al., 1998Porites porites-16 Marubini & Thake, 1999Porites compressa-27 Marubini et al., 2001Acropora sp.-37 Schneider & Erez, 2000Porites/Montipora-50 Langdon & Atkinson, in prep.CoccolithophoridsEmiliania huxleyi -10 Riebesell et al., 2000Gephyrocapsa oceanica -29 Natural pop. (N. Pac.) -38 Emiliania huxleyi -17 Zondervan et al., 2001Gephyrocapsa oceanica 29

    CommunityBiosphere 2 -40 Langdon et al., 2000Monaco mesocosm -21 Leclercq et al., 2000Bahama Bank -30 Broecker & Takahashi, 1966

  • Future pH ChangesBurn all known stocks of fossil fuels Atmospheric CO2 would exceed 1,900 parts per million around the year 2300pH reduction at the ocean surfaceCalcium carbonate skeletonsUnabated CO2 emissions Changes in ocean pH

  • ConclusionsCO2 Calcification

    for 200 to 280 matm pCO2 Calcif. 34%for 350 to 700 matm pCO2 Calcif. 58%

  • ConclusionsSaturation state (W) controls calcification Consequences of reduced calcification Space and lightSealevel riseErosion and damageDecomposition of Calcium Carbonate

  • Literature Cited Barker, S., Higgins, J.A., and Elderfield, H. 2003. The future of the carbon cycle: review,calcification response, ballast and feedback on atmospheric CO2. Philosophical Transaction of the Royal Society, 361, 19771999.

    Caldeira, K. and Wickett, M.E. 2003 Oceanography: anthropogenic carbon and ocean pH. Nature, 425, 365.

    Etheridge, D.M., ,Steele, L.P., R.L. Langenfelds, Francey, R.J., Barnola, J.M., and Morgan, V.I.. 1998. Historical CO2 records from the Law Dome DE08, DE08-2, and DSS ice cores. In Trends: A Compendium of Data on Global Change. Carbon Dioxide Information Analysis Center, Oak Ridge National Laboratory, U.S. Department of Energy, Oak Ridge, Tenn., U.S.A.

    Gattuso, J.-P., Allemand, D., and Frankigoulle, M. 1999. Photosynthesis and Calcification at Cellular, Organismal and Community Levels in Coral Reefs: A Review on Interactions and Control by Carbonate Chemistry. American Zoological Society, 39, 160-183.

    Gerin, F. & Edmunds, B. 2001. Mechanisms of interaction between macroalgae and scleractinians on a coral reef in Jamaica. Journal of Experimental Marine Biology and Ecology, 261, 159172.

  • Literature CitedKeeling, C.D. and Whorf, T.P. 2005. Atmospheric CO2 records from sites in the SIO air sampling network. In Trends: A Compendium of Data on Global Change. Carbon Dioxide Information Analysis Center, Oak Ridge National Laboratory, U.S. Department of Energy, Oak Ridge, Tenn., U.S.A.

    Langdon, C. 2001. Overview of experimental evidence for effects of CO2 on calcification of reef builders. Proceedings of the 9th International Coral Reef Symposium, Oct 23.27, 2000, Bali Indonesia.

    Marland, G., Boden, T.A., and Andres, R.J. 2006. Global, Regional, and National Fossil Fuel CO2 Emissions. In Trends: A Compendium of Data on Global Change. Carbon Dioxide Information Analysis Center, Oak Ridge National Laboratory, U.S. Department of Energy, Oak Ridge, Tenn., U.S.A.

    Marubini, H., Barnett, C., Langdon, M., and Atkinson, M.J. 2001. Dependence of calcification on light and carbonate ion concentration for the hermatypic coralPorites compressa. Marine Ecology Progress Series, 220, 153162.

    Marubini, F., Ferrier-Pages, C., and Cuif, J.-P. 2003. Suppression of skeletal growth in scleractinian corals by decreasing ambient carbonate-ion concentration: a cross-family comparison. Proceedings of the Royal Society of London B, 270, 179184.

    Petit, R., Jouzel, J., and Raynaud, D. 1999. Climate and atmospheric history of the past 420,000 years from the Vostok ice core, Antarctica. Nature 399, 429-436.

    This talk will focus on four areas: a general overview of the problem presented, structure of the coral animal, how seawater can buffer itself to maintain life, and how CO2 affects seawater and in turn, the coral animals of the reef.CO2 emissions have changed the chemistry of the atmosphere and are beginning to change the chemistry of the surface ocean. These changes could have a direct effect on the physiology of marine organisms.CO2 may increase rates of photosynthesis in regions where nutrients are not limitingCO32- may decrease rates of calcification because the alkalinity may drop to dangerous levels. Alkalinity helps to maintain pH and buffer seawater in order for calcium to be incorporated into the skeletons of coral.

    If these CO2 emissions produced were big enough, the balance between photosynthesis and calcification could be upset. Coral reefs could be the first ecosystems to feel the effects because of an altering to the carbonate buffering system of seawater as well as the following problems.

    Less able to keep up with sealevel rise. When global temperatures increase, it will eventually cause polar icecaps to melt which will cause seas to rise. With higher seas, less light will be able to reach coral reefs, which will decrease the rate and amount of photosynthesis. (Langdon, 2001)

    2. Less able to compete for space with faster growing algae. When carbonate buffering systems are not working properly, nuisance algae will grow and out compete corals for nutrients, calcium, and light. (Gerin and Edmumds, 2001)

    3. More susceptible to boring organisms and storm damage. Corals will not be able to grow a thick skeleton, which will lead to brittle animals. Storms will break limbs of coral easily, as well as boring invertebrates can puncture the coral skeleton much easier. (Marubini, et. al., 2003)

    The graph on the left indicates how levels of CO2 have fluctuated over the last 300000 years. As you can see, we are currently experiencing an increase in CO2 production because of a variety of impacts from humans.

    The graph on the right indicates the amount of CO2 produced in the last 1000 years. Recent human actions have caused a spike in the amount of CO2 produced. As you can see, it is higher than at any time in human history with no indications of slowing or decreasing. The elevated CO2 will cause devastating effects on our oceans, in particular, the coral reefs.As greenhouse gas emissions have increased since 1850 (the industrial revolution), CO2 has been the main contributor to these emissions. As with the previous slide, the amount of CO2 is at unprecedented levels as seen through human history.What we see as a large head (or colony) of coral is actually made up of thousands of tiny individual animals called polyps. These polyps range in diameter from about 1 mm to 1 cm or more. Each polyp looks somewhat like a small sea anemone, which is not surprising, as corals and sea anemones are cousins. Another member of the corals family is the jellyfish. All three of these groups contain stinging cells called nematocysts. Most corals nematocysts are not strong enough to penetrate human skin, so we cannot feel them sting, but they are able to use their nematocysts to defend against some predators and to catch food.

    Before we can talk about coral reefs, we need to start with a basic questionwhat is a coral? Is it animal, vegetable or mineral?The correct answer is that it can be all three. Corals are animals that may have a special relationship with a microscopic plant and that can make an external limestone (or mineral) skeleton.

    This relationship between corals and algae is a type of symbiosis. Both the coral and the algae (known as zooxanthellae) benefit from the partnership, so this is an example of a mutualistic symbiosis. The zooxanthellae are safe from predators inside the coral tissue (remember, corals have stinging cells) and the coral provides them with nutrients in the form of excreted nitrogen and phosphorus. In return, the zooxanthellae provide the coral with sugar compounds that they make when they photosynthesize.Most corals appear brown in color. This is a result of the millions of brown zooxanthellae that are found in their cells. Occasionally, when corals are stresses by high water temperature or other factors, the zooxanthellae will be lost, leaving the corals appearing almost pure white. This phenomenon is known as coral bleaching. The coral may die following bleaching, but often it will recover and become repopulated with zooxanthellae.

    By adding CO2 to water, it quickly converts to carbonic acid and dissociated to bicarbonate.

    So, as more CO2 dissolves, more protons are released and this acidifies the water. The carbonate combines with the protons and produces bicarbonate which decreases carbonate concentration. (Gattuso, et al, 1999)Dissolution of calcium carbonate in seawater is influenced by three major factors: temperature, pressure and partial pressure of carbon dioxide (CO2). The easiest way to understand calcium carbonate (CaCO3) dissolution is to recognize that it is controlled, in large part, by the solubility of CO2: CaCO3 + H20 + CO2 Ca++ + 2HCO3- The more CO2 that can be held in solution, the more CaCO3 that will dissolve. Since more CO2 can be held in solution at higher pressures and cooler temperatures, CaCO3 is more soluble in the deep ocean than in surface waters. Finally, as CO2 is added to the water, more CaCO3 can dissolve. The result is that, as more CO2 is added to deep ocean water by the respiration of organisms, the more corrosive the bottom water becomes to calcareous shells.

    Leads to a less stable reef structure and the dissolving of calcium carbonate.

    (Barker et al, 2003)

    Rising atmospheric CO2 leads to increased dissolution of CO2 into sea water. This changes the carbonate equilibrium in the oceans resulting in a decrease in alkalinity. Alkalinity is an important factor in coral skeletal growth. Alkalinity is a measuring of buffering potential and the amount of carbonate available to bind with calcium to deposit into coral skeletons. Alkalinity also buffers pH to keep seawater at a pH between 8.0 and 8.4. Lower alkalinity reduces the CaCO3 saturation state of water making it harder for coral reefs to grow. If there is not enough carbonate in the system, then calcium will not be pulled out of the water and deposited into the coral skeleton.

    (Langdon, 2001)The graph illustrates past relationships and well as possible future affects on seawater carbonate chemistry. As the concentration of CO2 increased, the saturation state of aragonite, which controls coral skeleton calcification, decreased. As the author extrapolates for possible future CO2 increases, the amount of calcium that is available for corals as diminishing. This study was completed assuming the normal state of seawater which has a salinity of 35 ppt and a total alkalinity of 3.5 meq/L

    (Langdon, 2001)Data taken from the Hawaiian Ocean Times Series Station that depicts the decrease of the saturation state of aragonite which leads to coral calcification. As the alkalinity decreases because of excessive CO2, the amount of calcium that is available for coral skeletons has decreased.

    (Langdon, 2001)In this experiment, Langdon altered the amount of CO2 in the atmosphere to determine the affects of CO2 on seawater carbonate chemistry and its relationship to seawater pH. He varied the pCO2 from roughly 200 uatm to 400 uatm, and 700 uatm. The results indicate that bicarbonate ions increase as CO2 increases because of the shift in equilibrium of the buffering system. The amount of carbonate ion decreases as well as pH when CO2 increases. This limits the alkalinity of the seawater system which ultimately affects coral skeleton calcification.

    (Langdon, 2001)Graphs shows the affects of increased amount of atmospheric CO2 on the calcification of a coral reef community. As the amount of CO2 increases, the rate of calcification also decreases. This will eventually cause coral skeletons to become very thin and fragile, or to stop coral growth altogether.

    (Langdon,2001)

    Another study showing the relationship between atmospheric CO2 and calcification. In this study, the CO2 was increased from 200 uatm to 700 uatm over a range of light intensities. The data show that the coral species Porites compressa had a lower rate of calcification when the amount of CO2 was elevated.Langdon, 2001 lists an accumulation of various other studies to show a doubling of CO2 on the rate of calcification. Multiple types of corals, and other marine invertebrates were used in these studies, they all showed a decrease in calcification when CO2 was increased. This indicates that the increased CO2 concentration in the earths atmosphere will have a deleterious effects on coral reefs and the marine invertebrates that inhabit these ecosystems.Caldiera and Wickett 2003 estimated what would happen if mankind were to burn all known stocks of fossil fuels as atmospheric CO2 would exceed 1,900 parts per million around the year 2300. This PCO2 would result in a maximum pH reduction at the ocean surface of 0.77 units. Coral reefs, calcareous plankton and other organisms whose skeletons or shells contain calcium carbonate would be affected. While a seemingly small change in pH, ice-core records and other paleoclimate data suggest that over the past 300 Myr there is no evidence that ocean pH was more than 0.6 units lower than today. Unabated CO2 emissions over the coming centuries may produce changes in ocean pH that are greater than any experienced in the past 300 Myr.

    Photosynthesis and calcification are not tightly coupled with respect to their response to rising CO2.CO2 Calcif.There is a nonlinear relationship between calcification and pCO2for 200 to 280 matm pCO2 Calcif. 34%for 350 to 700 matm pCO2 Calcif. 58%

    As more CO2 is added to the atmosphere, the amount and rate of calcification will decline which will have devastating affects of coral reef ecosystems. Coral skeletons will not be able to grow or recover from damage or attack. In addition, the loss of zooxanthellae will cause a decline in photosynthesis which will cause bleaching of corals. Once the bleaching has occurred, it is extremely difficult to keep the coral animal alive.

    Data are consistent with the hypothesis that saturation state controls the calcification of the coral reef system, several species of coral, calcareous red algae, and a natural community dominated by green algae.Consequences of reduced calcification to corals and coral reefs reduced ability to compete for space and lightreduced ability to keep up with sealevel riseincreased susceptibility to erosion and damage by fish, boring organisms and storms.

    From a geochemical point of view the reduction in the ratio of calcification to net photosynthesis as CO2 rises provides a negative feedback on atmospheric CO2 levels. What occurs is that more CO2 will be released into the atmosphere because the carbonate buffering system cannot handle the decomposition of calcium carbonate. The calcium carbonate will leach back into the seawater and eventually be released as CO2 into the atmosphere, therefore causing an even high level of CO2 and creating an even greater warming affect on the planet.