9 |
The Carbonate System of the Ocean |
| K. WAGENER |
| ABSTRACT | |
| 9.1 GENERAL | |
| 9.2 THE BUFFER SYSTEM | |
| 9.3 EFFECT OF HIGHER CO2 PARTIAL PRESSURES ON THE pH OF SEA-WATER | |
| REFERENCES | |
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Item (i) has been studied on the basis of the 14C distribution in the ocean, using different models of oceanic structure and mixing. In general, the rapid equilibration between atmophere and the mixed surface layer (between 5 and 10 years) is no matter of dispute, while the calculated deep-sea mixing rates are much more dependent on the type of model. The residence time in the deep sea is between 500 and 2000 years. The deep-sea mixing rate still seems to be a parameter which can easily be adjusted to account, at least partly, for the uptake of additional CO2 as released from the changing biosphere (besides the fossil production). The biosphere under human impact has recently been identified as an intensive CO2 source (Woodwell et al., 1978; Bolin, 1977). Its CO2 production has been calculated from 13C measurements by Stuiver (1978), Wagener (1978), and Freyer (1978).
Item (ii) is also a complex property, because of the intricate buffer system involved. In spite of the basic importance of this property there are only very few direct measurements of the CO2 buffer capacity of sea-water. Further data are urgently needed, since recent results have indicated that the buffer capacity is higher than previously estimated, which means a faster rate of CO2 uptake by the ocean (Rebello and Wagener, 1976, 1978b).| CO2 (g) |
(1) |
|
CO2 (aq) +H2O |
(2) |
| H2CO3 |
(3) |
| HCO3 |
(4) |
| H2O |
(5) |
while the primary buffering is realized through the process
|
CO2 (aq) + H2O +CO2 |
(6) |
Metal-carbonate ion pairing influences the effective concentrations of
HCO3
and also, to some degree, the pH (Whitfield, 1974), so that the buffering capacity also depends on the salinity of sea-water. The limitation of the buffering capacity is given by the limited supply of
CO3
(under natural conditions about 13% of the inorganic carbon present). In surface sea-water, biological activity consumes
CO2 and shifts reaction (6) to the left, so that cold surface water is depleted in
HCO 3
but rich in CO2
3, and thus supersaturated with CaCO3. Average concentrations in cold surface water are
(Broecker, 1974):
[CO2
3]=
|0.00| 020 mole/l
If this water descends (e.g. in the Weddell Sea), respiration and decay processes produce CO2, and with increasing depth and/or increasing residence time below the euphotic zone, reaction (6) is shifted to the right. As a result, water of intermediate depth is more or less saturated with CaCO3, while deep water is unsaturated. Average concentrations in deep water are (Pacific):
[HCO3 [CO2
3] = 0.00 010
moles/l
Attack of sediments (solution of CaCO3) can be excluded for the time scale under consideration. An accurate calculation of the buffering behaviour of sea-water (Keeling, 1973) must include the contributions of the borates, and interactions with minor species.
In global models for the prediction of future CO2 levels, the interaction between sea-water and a variable CO2 partial pressure is usually characterized by the ratio of fractional changes in the atmosphere and the surface water,
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where P= CO2 partial pressure, and
c =
[HCO
3] +
[CO2
3]
+CO2 (aq)]. Various authors, however, use different normative values
(preindustrial or actual values, respectively) which give different numerical values for that ratio. Moreover, using the same name for different definitions presents a source of confusion.
Table 9.1 summarizes all definitions and names and gives numerical data.
It turns out that recent experimental data on the buffer factor is lower by (17 ± 2) % than that generally accepted in the literature (Rebello, 1978b). An evaluation of Kanwisher's (1960) measurements gives a much higher figure (see Table 9.1). The importance of the buffer factor for estimating the exchange behaviour of the ocean is obvious, and additional measurements are most desirable.
All figures of Table 9.1 depend on P and temperature. A figure which was found independent of
P and temperature in the range 10
°C < 5 T < 30
°C and for 200 ppm < P
2400 ppm is
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=d ln P |
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=3876±500 | ||
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d |
(Rebello, 1978a).
*
can be converted into the other definitions listed in Table
9.1:
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P |
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Po |
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• |
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ln(P/Po) |
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| z = |
P |
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Po |
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| B = | |||
It is important to note the dependence of the evasion factor,
, which is the figure most frequently used to describe the buffer behaviour of sea-water on
P or
c respectively.
Figure 9.1 shows measurements on South Atlantic surface water up to 6000
ppm. The curve is an 8th-grade fitting polynome, from which the evasion factors have been calculated
(Figure 9.2). The evasion factors for 25.6
°C are lower than those calculated by Keeling (1973) for 19.6 °C by about 15%. The temperature effect on
, however, seems to be small, so that the buffer capacity indeed
seems to be higher than presently accepted. Again, more measurements are extremely desirable.
Table 9.1 Different definitions and forms to describe the interaction between
CO2 and surface ocean water, as used by various authors. P,
CO2 = actual values; Index° refers to preindustrial data. The given numerical values refer to conditions and data as indicated
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| Numerical | Conditions for the given | |||||
| Author | Definition | Name | value | numerical value | ||
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| Revelle and Suess | Revelle factor | ~10 | Estimated for average data of | |||
| (1957) |
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sea-water | ||||
| Bolin and Eriksson | 12.5 | constant A = 2.37 mval/1 | ||||
| (1959) |
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| borates neglected | ||||||
| Kanwisher (1960) | (His experimental results | |||||
| evaluated for the evasion factor, |
16.3 | 31.5‰ salinity | ||||
| 10 and 20 °C (giving same result) | ||||||
| 330 ppm CO2 | ||||||
| Broecker et al. |
d In P |
Buffer factor | 9.2 | average ocean surface water | ||
| (1971) | B = |
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330 ppm CO2 | |||
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d In |
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| Bacastow and Keeling | (Pm-Pom)/Pom | Evasion factor | 9.7 | 330 ppm; A =constant | ||
| (1973) |
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average ocean surface water | ||||
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( |
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| Keeling (1973) |
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Buffer factor | 10.3 | average ocean surface water | ||
| z = |
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330 ppm; A =constant | ||||
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| Pytkowicz (1977) | (Buffer factor)-1 | 10.01 | A = 2.331 mval/kg sw | |||
| 19.26‰ chlorinity | ||||||
| pH = 8.262; T = 17.70 °C | ||||||
| Rebello and Wagener | Measurements in the range 300 < p < 400 ppm | B = 7.8 ± 1.0 | 7 sea-water samples from different | |||
| (1976) |
evaluated for the evasion factor, |
locations; 330 ppm | ||||
| buffer factors, z, B | z=8.87 ± 1.2 | |||||
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Figure 9.1 Measurements of P vs.
COa on South Atlantic surface water sampled 1 Sept. 1977, at Barra da Tijuca near Rio de Janeiro. Total alkalinity = 2.33
mM,
CO2 = 45 ml/1; total boron = 5.0 ± 0.1 ppm. Preliminary results of Rebello (1978b). The curve is an 8th-grade fitting polynome
Figure 9.2 Evasion factors (for definition see Table 9.1) as a function of the CO2 partial pressure. Po = 295 ppm. Upper two curves - broken line, evaluation of Kanwisher's measurements (1960) on a sea-water sample of 31.5‰ salinity; solid line, same results corrected for 36.2‰ salinity. Keeling's data from Keeling (1973). Lower curve (Rebello, 1978b) derived from the fitting polynome in Figure 9.1
Figure 9.3 log P vs. pH as derived from equilibrium measurements of Rebello (1978b). Open circles: measurements of Figure 9.1 (South Atlantic surface water, 25.6 °C); full circles: North Sea water, 20 °C
It has been argued that, as a consequence of higher CO2 partial pressures, the surface layers of the ocean may become undersaturated with respect to calcium carbonate, according to equation (6), with possible catastrophic biological consequences (Bacastow and Keeling, 1973; Fairhall, 1973; Zimen and Altenhain, 1973; Broecker et al., 1971). Whitfield (1974), however, calculates that this will not happen in the foreseeable future. Any change in the carbonate/bicarbonate ratio also means a change in pH. On the assumption that at any point in time in the mixed layer the equilibrium with the atmospheric CO2 concentration is established, and using the prediction of Machta (1972) on future CO2 levels, Whitfield finds for the change of pH:
A.D. 1958: [CO 2 (g)] = 313 ppm;pH = 8.24
A.D. 2010: [CO2 (g)] = 453.5 ppm; pH = 8.16
This gives
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0.161 |
Laboratory measurements under equilibrium conditions gave for this ratio 1.0; see
Figure 9.3. Both Whitfield's calculation and the experiments exclude the interaction with solid CaCO3. From equation (7) below (for references
and data see Skirrow, 1975) one finds
pH/
log
P = -0.88 for pH > 8 and -0.95 for pH < 8:
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aH |
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| P = | C A |
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(7) |
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K'1 • |
where CA = carbonate alkalinity = [HCO
3] +
2 [CO2
3] ; K'1 , K'2 = first and second
apparent dissociation constant of carbonic acid;
= solubility coefficient of CO2 in sea-water.
The ecological consequences of a possible change in the calcium carbonate supersaturation, with respect to calcareous organisms, can only be examined experimentally. From general aspects, it seems unlikely that CaCO3. supersaturation is a precondition for carbonate biomineralization for the following three reasons: (i) life processes are far out of equilibria; (ii) biomineralization depends on the active transport of ions through biomembranes driven by metabolic energy, and thus do not depend on the free energy of any carbonate reaction; (iii) calcium carbonate structures of living organisms may be covered by organic tissue, representing a barrier against fast exchange processes.
Again, it is important to note in this context the recent indications which suggest that the ocean might be a stronger sink for CO2 than believed so far, able to take up the additional CO2 production from the shrinking biosphere.
Bacastow,R. and Keeling, C. D. (1973) Atmospheric carbon dioxide and radio-carbon in the natural carbon cycle. II: Changes from A.D. 1700 to 2070 as deduced from a geochemical model. In: Woodwell, G. M. and Pecan, E. V. (eds), Carbon in the Biosphere. AEC Symposium Series 30, 86-136. NTIS U.S. Dept. of Commerce, Springfield, Virginia.
Bolin, B. (1977) Changes of land biota and their importance for the carbon cycle. Science 196, 613-615.
Bolin, B. and Eriksson, E. (1959) Changes in the carbon dioxide content of the atmosphere and the sea due to fossil fuel combustion. In: The Atmosphere and the Sea in Motion, 130-142. Rockefeller Institute Press, New York.
Broecker, W. (1974) Chemical Oceanography, 1-214. Harcourt Brace Jovanowich, Inc., New York.
Broecker, W. S., Li, Y.-H., and Peng, T.-H. (1971) Carbon dioxide
man's unseen artifact. In: Hood, D. W. (ed.),
Impingement of Man on the Oceans, 287-324. Wiley Interscience, New York.
Fairhall, A. W. (1973) Accumulation of fossil CO2 in the atmosphere and the sea. Nature 245, 20-23.
Freyer, H. D. (1978) On the 13 C record in tree rings. I:13C variations in northern hemispheric trees during the last 150 years. Preliminary evaluation of the past CO2 increase. Unpublished manuscript. To be submitted to Tellus.
Kanwisher, I. (1960) P CO2 in the sea-water and its effects on the movement of CO2 in nature. Tellus 12, 209-215.Keeling, C. D. (1973) The carbon dioxide cycle: reservoir models to depict the exchange of atmospheric carbon dioxide with the oceans and land plants. In: Rasool, S. J. (ed.), Chemistry of the Lower Atmosphere, 251-329. Plenum Press, New York, London.
Machta, L. (1972) The role of the oceans and the biosphere in the carbon dioxide cycle. In: Dyrssen, D. and Jagner, D. (eds), The Changing Chemistry of the Oceans. Nobel Symposium 20, 121-145. Almqvist and Wiksell, Stockholm.Pytkowicz, R. (1977) Private communication.
Rebello, A. de Luca and Wagener, K. (1976) New measurements on the system CO2 /sea-water. Thalassia Jugoslavica (in press).
Rebello, A. de Luca (1978a) CO2/sea-water interaction: new results. Z. Naturforsch. (in press).Rebello, A. de Luca (1978b) CO2 uptake capacity of sea-water under higher CO2 partial pressures. (UNpublished manuscript).
Revelle, R. and Suess, H. E. (1957) Carbon dioxide exchange between atmosphere and ocean, and the question of an increase of atmospheric CO2 during the past decades. Tellus 9, 18-27.Skirrow, G. (1975) The dissolved gases
carbon dioxide. In: Riley, J. P. and
Skirrow, G. (eds), Chemical Oceanography, vol. 2, 2nd ed., 1-192.
Academic Press, London, New York, San Francisco.
Wagener, K. (1977) Total anthropogenic CO2 production during the period 1860-1975 from carbon-13 measurements. Rad. and Environm. Biophys. (in press).
Whitfield, M. (1974) Accumulation of fossil CO2 in the atmosphere and the sea. Nature 247, 523-525.Woodwell, G. M., Whittaker, R. H., Reiners, W. A., Likens, G. E., Delwiche, C. C., and Botkin, D. B. (1978) The biota and the world carbon budget. Science 199, 141-146.
Zimen, K. E. and Altenhain, F. K. (1973) The future burden of industrial CO2 on the atmosphere and the oceans. Z. Naturforsch. 28a, 1747-1752.|
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