David Archer
Department of the Geophysical Sciences, University of Chicago, IL
Haroon Kheshgi
Exxon Research and Engineering Company, Annandale, NJ
Ernst Maier-Reimer
Max-Planck-Institut für Meteorologie, Hamburg, Germany
Abstract. The long term abiological sinks for anthropo-genic CO2 will be dissolution in the oceans and chemical neutralization by reaction with carbonates and basic igneous rocks. We use a detailed ocean / sediment carbon cycle model to simulate the response of the carbonate cycle in the ocean to a range of anthropogenic CO2 release scenarios. CaCO3 will play only a secondary role in buffering the CO2 concentration of the atmosphere because CaCO3 reaction uptake capacity and kinetics are limited by the dynamics of the ocean carbon cycle. Dissolution into ocean water sequesters 70-80% of the CO2 release on a time scale of several hundred years. Chemical neutralization of CO2 by reaction with CaCO3 on the sea floor accounts for another 9-15% decrease in the atmospheric concentration on a time scale of 5.5 - 6.8 kyr. Reaction with CaCO3 on land accounts for another 3-8%, with a time scale of 8.2 kyr. The final equilibrium with CaCO3 leaves 7.5-8% of the CO2 release remaining in the atmosphere. The carbonate chemistry of the oceans in contact with CaCO3 will act to buffer atmospheric CO2 at this higher concentration until the entire fossil fuel CO2 release is consumed by weathering of basic igneous rocks on a time scale of 200 kyr.
The release of fossil fuel CO2 was simulated by increasing the atmospheric CO2 concentration following projections from IPCC 1990 [Houghton et al., 1990] to the year 2100, and in some cases extrapolating the year 2100 emission for one or two centuries more, for net releases of 900, 1500, 3000, and 4500 Gton C as CO2, approaching the estimated 5000 Gton C of potentially recoverable coal, oil and gas [Sundquist, 1985]. The IPCC scenarios incorporated projections of biospheric uptake, but for simplicity no further biospheric uptake was allowed following the end of the emission period, as the model was run to the year 40,000 for the 3000 Gton scenario and the year 10,000 for the others (Figure 1a). All scenarios were also run to the year 10,000 in the absence of weathering and burial of CaCO3.
This model is a more quantitative accounting of the effect of ocean chemistry on atmospheric pCO2, and of the reservoirs and fluxes of carbon in the deep sea, than has been applied previously to predicting the fate of anthropogenic CO2. For example, we find that after an initial relaxation time, the dissolution flux from the sea floor is regulated in part by deep ocean flow , an effect best simulated using a three dimensional circulation model. Recent work [Archer, 1996] shows that CaCO3 dissolution kinetics are slower than had been used in previous models, and presumably therefore less responsive to CO2 invasion. Also the inventory of CaCO3 on the sea floor available for dissolution is a factor of three smaller than the value used in previous neutralization projections. Using these refinements, we hope to reduce the factor of four range in published estimates of the time scale for CaCO3 compensation [Broecker and Peng, 1987; Keir, 1988; Sundquist, 1990].
In the ocean, CaCO3 is found in nearshore sediments such as coral reefs, and in sediments of the open ocean at depths shallower than the undersaturated abyssal waters. Respiration-driven dissolution in shallow water sediments could be enhanced by a decrease in overlying water supersaturation [Walter and Burton, 1990], but the greater area of CaCO3 rich sediments in the deep sea, and the under-saturation of the deep ocean, argue that the shallow water contribution to fossil fuel neutralization will be smaller than that of the deep ocean. We make the simplifying assumption of neglecting it altogether.
The inventory of CaCO3 on the deep sea floor which is available for dissolution is determined by the geometry of surface sediments. Bioturbation (sediment mixing by benthic macrofauna) exposes CaCO3 from roughly 10 cm depth [Berger and Killingley, 1982] to the zone of dissolution at the sedi-ment surface on time scales of hundreds of years. If the trans-ient dissolution flux following CO2 invasion exceeds the mass sedimentation rate to the sea floor, then old CaCO3 can be exposed from below the bioturbated layer in a process called chemical erosion, which can potentially continue until the bioturbated layer becomes filled by non-CaCO3 material, iso-lating CaCO3 from the zone of dissolution. The inventory of erodable deep sea CaCO3 in the model is approximately 1770 Gton C, comparable with a value of 1600 Gton C from a recent reassessment of sea floor data [Archer, 1996] (and a factor of three smaller than the Broecker and Takahashi [1978] estimate used in previous estimate fossil fuel uptake studies [Broecker and Peng, 1987; Sundquist, 1990; Walker and Kasting, 1992].
Chemical erosion is a transient condition which continues until the CaCO3 supply to the bioturbated layer as sedimenting particles is balanced by losses due to dissolution and burial. This condition is hereafter referred to as local lysocline equilibrium. The global bioturbated layer CaCO3 inventory in local lysocline equilibrium, determined from direct model experiments, is plotted as a function of the deep sea CO3= concentration in Figure 3a. Superimposed upon this are model time trajectories from Figure 1. The model came close to local lysocline equilibrium by the year 10,000 in all cases. Most of the change in ocean chemistry during this time can be attributed to the decrease in sea floor CaCO3 inventory, defining this time period as the sea floor neutralization stage. After the lysocline reaches local equilibrium with the water column, as marked by the intersection of the model trajectories with the local lysocline equilibrium line, there is no longer a thermodynamic driving force for further chemical erosion, and both the ocean CO3= and the sea floor CaCO3 inventories await replenishment by the imbalance between weathering and accumulation (terrestrial neutralization), as can be seen by the change in the path of the model trajectories toward higher inventories in Figure 3.
If the fossil fuel CO2 release is less than our maximum 4500 Gton C value, then only a fraction of the "potentially available" CaCO3 can dissolve before the end of sea floor dissolution associated with reestablishment of local lysocline equilibrium (Figure 3b). Sea floor neutralization sequestered 10-15% of the atmospheric concentration of anthropogenic CO2 (greater for larger CO2 release: Figure 2). A log-linear plot of the approach of atmospheric CO2 to final neutralized values (discussed below) reveals [[tau]] values in the sea floor neutralization stage (before A.D. 10k) of 5.5 - 6.8 kyr, and a value of 8.3 kyr for the A22 scenario for the terrestrial neutralization stage (after A.D. 10k). These time scales could be decreased by dissolution of shallow water carbonates or a climate-related increase in terrestrial weathering or perturbed, probably increased, by changes in deep sea circulation driven by anthropogenic climate change [Manabe and Stouffer, 1993]. The magnitude of the atmospheric decrease is most sensitive to the availability of CaCO3 for dissolution, determined in the deep sea by the depth of bioturbation and the porosity of surface sediments.
(1)
where KH, K1, and K2 are the Henry's Law and first and second dissociation constants for CO2 and carbonic acid. Based on this, the ratio of the final and initial atmospheric CO2 inventories can be written
(2)
where ocean [CO3=] is held constant by equilibrium with CaCO3, and the relative increase in HCO3- is approximated by the increase in the ocean CO2 inventory ([[Sigma]]CO2). Cff is the magnitude of the anthropogenic CO2 release, and the factor of 2 is derived from the nearly 1:1 stoichiometry of CO2 reaction with CaCO3, eventually releasing two carbons to the ocean per carbon of fossil fuel. Taking atm CO2i as 625 Gton C, [[Sigma]]CO2i as 38,000 Gton C, and CO2ff as ranging from 800-4,500 Gton C, we estimate that the atmospheric partition of fossil fuel carbon should be between 6.7-7.3% after complete neutralization, consistent with the model result.
In nature, the residual atmospheric CO2 will ultimately be consumed by the silicate rock cycle, which maintains a long-term balance between CO2 degassing from the mantle and CO2 uptake by weathering of calcium and magnesium silicates by reactions such as CaO (silicate rock) + CO2 -> sedimentary CaCO3. This mechanism is thought to stabilize atmospheric pCO2 with [[tau]] = 200 kyr. Approximating the silicate weathering mechanism as a simple 200 kyr exponential approach to an atmospheric pCO2 of 280 ppm, the time dependent response of the atmospheric pCO2 to a 3,000 Gton anthropogenic CO2 IPCC injection scenario (scenario A22) can be written as
(3)
(Figure 4) where the four terms in brackets represent the time dependent uptake by ocean invasion, sea floor and terrestrial CaCO3 neutralization, and silicate weathering, respectively.
While this expression summarizes our best estimate of known long-term sinks of CO2, it does not account for the observed modulation of atmospheric CO2 concentration over the glacial cycles [Barnola et al., 1987] which are poorly understood and which highlight our limited ability to predict long-term atmospheric CO2. Nevertheless, we can predict that the carbonate chemistry of the oceans in contact with CaCO3 will act to buffer atmospheric pCO2 at these higher levels. In order for the terrestrial biosphere or silicate rock weathering, for example, to restore atmospheric CO2 to its preanthro-pogenic value, we require uptake not only of the atmospheric CO2 excess, but of the entire fossil fuel CO2 load, including that which has reacted with CaCO3, reducing the cumulative net atmospheric release to zero. If the atmospheric fraction of the fossil fuel CO2 (atmCO2t) is removed from the atmosphere, degassing from the ocean and precipitation of CaCO3 would replenish most of the drawdown of atmCO2t. Future variability in the global carbon cycle, such as accompanied the glacial cycles, would then drive atmospheric CO2 perturbations starting from a new robust baseline value, atmCO2t.
Acknowledgements. This work was supported in part by the Petroleum Research Fund and the National Center for Atmospheric Research. We thank several anonymous reviewers for helpful criticism.
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(Received October 7, 1996; revised January 13, 1997;
accepted January 16, 1997)