The short carbon cycle: the ocean link.

E&ES 359 Climate Change J. C. Varekamp

In the 1980-1990 period we released on the order of 5.4 GtC from fossil fuel burning and 1.0 GtC from deforestation, for a total of 6.4 GtC/yr. From the observed data of CO2 in the atmosphere, we can deduce that about 3.3 GtC stayed in the atmosphere (about 52 %), and models predict that about 2.1 GtC disappeared into the oceans (about 33 %). That leaves 1.0 GtC unaccounted for, and the only place where such a massive amount of carbon could have gone is in the biosphere (greening and browning of the earth, about 15 %).

It is hard to document the quantitative increase in terrestrial biosphere mass and the ocean uptake term is model dependent as well. How do we figure this all out?

  1. The Keeling (p) curve from 1957 till now shows the steady increase in atmospheric CO2 and the seasonal oscillation caused by the waxing and waning of the northern hemispheric terrestrial biomass (remember our discussion here about distribution of land and biosphere). There are slight indications that the seasonal amplitude has increased over time, suggesting an ‘earth greening’ process.
  2. In 1988 Keeling (f) discovered a method to measure small changes in atmospheric O2 and his atmospheric O2 curve is out of phase with the Keeling (p) curve, which makes sense. We can predict the decrease in atmospheric O2 from the overall anthropogenic C flux, and the observed decrease is smaller than the predicted one: evidence for greening!! The observational record is too short to make better predictions for a partition of C sinks between ocean and the terrestrial biosphere. Some papers have appeared arguing that most of the CO2 went into the biosphere and not into the ocean, but these are highly debated.
(Calculate the CO2 uptake % in biomass if DpO2/DpCO2 equals 2.5)

The ocean uptake term can be approached from several angles. From thermodynamics we can calculate the C storage capacity of ocean water for the various carbonate compounds. This is a theoretical upper limit and does not tell us anything about the rate of uptake. The carbonate reactions are

CO2 + H2O è H2CO3èH+ + HCO3- è H+ + CO3=

These are known as the KCO2, K1 and K2 reactions, and the reaction constants are known for a given temperature. Total dissolved carbonate, SCO2, is H2CO3 + HCO3- + CO3=, and usually HCO3- is the largest of these three. We can calculate for a given pCO2 all the concentrations using the reaction constants and their equations, and the charge balance equation. The pH is also determined by the pCO2: when SCO2 increases, the pH goes down. The oceanic CO2 uptake capacity is usually expressed with the Revelle buffer factor, which is defined as the relative increase in SCO2 compared to the relative increase in atmospheric pCO2 or (DpCO2/pCO2) / (DSCO2 / SCO2 ) = ~11.

The changes in oceanic SCO2 are difficult to determine from carbonate measurements in sea water because the increases are small. Current SCO2 is about 140 ppm HCO3- and varies by a few ppm from spot to spot dependent on biological activity. The parameter of interest is the CO2 invasion rate, I, or how fast does CO2 dissolve in ocean water (reaction KCO2, K1 and K2 above) if there is a certain degree of undersaturation in the water relative to the pCO2 in the atmosphere. The uptake of CO2 can then be modeled as a function of I for some thickness of a mixed surface layer, and then the diffusion (D) of that CO2 through water to deeper layers. This would be a 1-dimensional, static ocean with no currents. The greatest resistance (slowest process) is the diffusion-into-deep-water term in these equations. Mixing in the surface waters is fast relative to the dissolution speed of CO2 so the top layer remains homogeneous. The factor I is obtained from the step wise modeling of absorption of CFC’s (a very different gas than CO2), Rn (a naturally occurring radioactive gas, different from CO2), Tritium (from nuclear experiments, but also a very different gas from CO2), from 14C generated during the bomb tests (1951-1964), and from natural 14C and its dilution by fossil fuel carbon in the atmosphere. The figure handouts show some of the details of these approaches: the bomb 14C pulse is the simplest: we can measure how far the bomb 14C has penetrated into the ocean (about 380 m), which gives the diffusion coefficient D, and we can measure the mean amount of 14C in the mixed layer, knowing for every year the 14C/C ratio in the atmosphere, which gives I (about 0.064 mole m-2 yr-1 Dmatm-pCO2-1). The Dmatm-pCO2 is the difference between atmospheric pCO2 and the virtual pCO2 in ocean water ([H2CO3]/KCO2). We can also model the abundances of natural 14C in the ocean, which becomes diluted with fossil fuel "dead" carbon. All of these approaches give similar I and D values. In our class experiments we determine directly the I value for a given temperature for different Dmatm-pCO2 values.

In addition to the static ocean model, we can consider the thermohaline convection component which drags surface waters to the ocean bottom. The surface waters may have absorbed some excess CO2 before they are dragged down, which is another sink for excess CO2 atm. The "conveyor belt of water" takes out 20 Sverdrups, which is 20 1016 m3/sec and we can calculate that as a potential annual CO2 sink of about 0.5 GtC (depends on the degree of equilibration with the atmosphere on the surface). Using all these numbers and models leads to the annual values of about 2.0 GtC into the ocean.

In addition to the CO2 dissolution fluxes, there is the biological carbon pump, which transports CO2 down into the ocean after photosynthesis. This process is strongly dependent on the availability of the nutrients NO3- and P, and is not directly influenced by the pCO2 in the atmosphere. The combustion of fossil fuels also delivers NOx to the atmosphere which then forms NO3-, which may lead to additional productivity and an enhanced biological carbon pump in the oceans. The strength of that mechanism to remove excess anthropogenic carbon is a matter of debate.