Effects of CO 2 on marine animals Time scales, processes, and limits of adaptation Hans O. Pörtner, Martina Langenbuch, Basile Michaelidis Alfred-Wegener-Institute,

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Presentation transcript:

Effects of CO 2 on marine animals Time scales, processes, and limits of adaptation Hans O. Pörtner, Martina Langenbuch, Basile Michaelidis Alfred-Wegener-Institute, Bremerhaven, Germany, Aristotle University of Thessaloniki, Greece. Interactions with temperature and hypoxia regimes Scenarios: Business as usual, Direct disposal, Indirect disposal (Fe fertilization)

Principle considerations: Role of time scales in CO 2 exposure experiments Incipient lethal CO 2 level (long term critical threshold) arbitrary units Mortality independent of exposure time Zone of resistance Mortality dependent on CO 2 level and exposure time Zone of tolerance Upper median lethal CO 2 level (LD 50 ) log exposure time (days, weeks, months, years) No such complete data set exists Tolerable organism and ecosystem (?) responses critical level and mechanism unknown Asphyxiation: squid and fish Pörtner, in prep.

Example of an animal species tolerant to CO 2 oscillations: Sipunculus nudus eurybathic: found between 0 and 2300 m depths

However, tolerance is limited: Delayed onset of enhanced mortality during long term disturbed maintenance under 1 % CO 2 in S. nudus Control 1 % CO 2 early 1% CO 2 late 3 % CO 2 % Mortality Days of incubation no decrease in body energy stores behavioral incapacitation involved Langenbuch et al. (2004) Control animals repeatedly reburying into sediment

Permian- Triassic mass extinctions Loss of marine invertebrate genera due to CO 2 ? moderately active, moderate calcification sessile, hypometabolic, calcified: larger effect? after Knoll et al., 1996 Physiological characters of eliminated forms? severest losses CO 2 limitations relevant in evolution? CO 2 limitations relevant in evolution? Number of genera

S. nudus: Extra- and intracellular acid-base status during hypercapnia in vivo after Pörtner et al partial compensation full compensation Partial compensation of extracellular acidosis: A typical finding in invertebrates? Physiological background??

55 % (!) growth reduction in Mytilus galloprovincialis under hypercapnia (permanent extracellular acidosis!!) Water pH 7.3: Maximum pH drop as expected from business as usual scenarios by 2300 (Caldeira and Wickett, 2003) hypercapnia control © M.S. Calle Michailidis et al. (2004)

Close correlation between dry / wet weight and shell length Reduced growth affects shell and soft body alike Michailidis et al. (2004)

Reduced cellular protein synthesis during acidosis favouring amino acid catabolism in S. nudus ….likely causing reduced growth rates Langenbuch et al

Mytilus galloprovincialis under hypercapnia (water pH 7.3): 65% (!) metabolic depression associated with enhanced N excretion, i.e. protein degradation during permanent (extracellular) acidosis (as seen in S. nudus) hypercapnia control hypercapnia control © M.S. Calle Michailidis et al. (2004)

Uncompensated intracellular acidosis in cuttlefish (S. officinalis) brain under 24 h of hypercapnia (1%) intracellular pH Sepia officinalis S. Schmidt, C. Bock, H.O. Pörtner, unpubl. Animals died despite return to normocapnia!!!

Uncompensated acidosis and metabolic depression in several invertebrates …contributing to lower resistance and enhanced mortality? Compensated acidosis and, therefore, no metabolic depression in most fish …a reason for enhanced resistance to high CO 2 ? Sepia officinalis Sipunculus nudus Pachycarabrachycephalum Gadus morhua ©CephBase see Poster Heisler, 1986, Larsen et al. 1997, Ishimatsu et al., 2004 Mytilus galloprovincialis

Mortality involves metabolic and behavioral depression caused by adenosine accumulation in nervous tissue of S. nudus Reipschläger et al., 1997 Reduced exercise capacity and activity

Unifying principles of CO 2 effects in animals …..mechanisms also affected by hypoxia and temperature extremes!! still incomplete!! Pörtner et al. 2004

A recent hypothesis: The first level of thermal intolerance at low and high temperature extremes in METAZOA is a loss in whole organism aerobic scope, a unifying principle in ectotherms (!) and endotherms (!?). Am. J. Physiol 279, R1531-R1538, Naturw. 88, , 2001 Am. J. Physiol. 283, R1254- R1262, 2002 Comp. Biochem. Physiol. 132A, , 2002 Temperature, hypoxia, CO 2 interactions?

Temperate crustacean, Maja squinado Temperate cephalopod, Sepia officinalis Antarctic bivalve, Laternula elliptica Atlantic cod, Gadus morhua Antarctic and temperate zoarcids, Pachycara brachycephalum, Zoarces viviparus EXAMPLES O 2 dependent temperature limits verified across phyla: annelids, sipunculids, molluscs (bivalves, cephalopods), crustaceans, fish and some air breathers, limited evidence in endotherms incl. man.

0 % oxygen limited aerobic scope TcTc TpTp TpTp : Peius Ts: onset of limitation in aerobic scope TcTc : Critical Ts: affecting growth, exercise, behaviours, reproduction, ….fitness Temperature onset of anaerobic metabolism after Frederich and Pörtner 2000, Mark et al Pörtner et al. 2000, Pörtner 2001, Cardiac + ventila- tory output 0 functional capacity of oxygen supply Q rest Q max after Farrell max Aerobic scope and performance are maximal at the upper peius temperature. rate of aerobic perfor- mance 0 temperature Hypoxia, CO 2 and thermal extremes act synergistically via the same physiological mechanisms!! Hypoxia, CO 2

Processes and Limits: Effects of integrated CO 2, O 2 and temperature fluctuations CO 2 impacts on: Hypoxia tolerance Improved extension of passive survival (limited!) BUT Aerobic scope Long term performance and growth functions Thermal tolerance (tolerance to thermal fluctuations ) These interactions and not CO 2 alone have likely shaped evolutionary scenarios! Pörtner and Langenbuch, in prep.

Animal limitations in high CO 2 oceans Progressive (not beyond critical thresholds?) effects already expected in 450 to 750 ppm surface ecosystems shifted ecosystem equilibra caused by: -reduced calcification rates -higher ratios of non-calcifiers over calcifiers -reduced tolerance to thermal extremes -enhanced geographical distribution shifts -reduced distribution ranges -reduced behavioral capacity, growth, productivity and life span * -food chain length and composition* -reduced population densities, ……biodiversity (critical!)?* *effects transferred to deep with ocean disposal (direct and indirect) Research needs to further identify mechanisms, titrate/quantify (lab and field) scenarios, address micro-evolutionary potential Pörtner and Langenbuch, in prep.

Ocean CO 2 disposal: Are their methods of choice? Preliminary insight from CO 2, T, hypoxia impact studies in animals Avoid business as usual scenarios (thermal changes, direct impact of CO 2 !) Avoid large scale disposal strategies (towed pipe or Fe fertilization) If feasible, use CO 2 lake option in environments protected from physical disturbance (dump site strategy) Apply direct pH neutralization of injected CO 2 ? Dispose in thermally stable environments Avoid hypoxia aggravation (eutrophication) Pörtner and Langenbuch, in prep.

CLIMATE CHANGE, CO 2 effects, ENERGY BUDGETS Dr. Christian Bock Carsten Burkhard Dr. Martina Langenbuch Dr. Anke Reipschläger SusannSchmidt Rolf-M. Wittig Dr. Vasilis Michailidis