3.2 Dissolved Gases

Gases in the Ocean

The ocean exchanges gases with the atmosphere across the air-sea interface, dissolving O₂, N₂, CO₂, and noble gases. The solubility of each gas depends on temperature, salinity, and pressure, following Henry's law. Once dissolved, gases are transported by ocean circulation and modified by biological processes—photosynthesis produces O₂, respiration consumes it, and the biological pump transfers carbon to the deep ocean.

Dissolved gas measurements serve as powerful tracers for ocean circulation, ventilation rates, and biological activity. Transient tracers such as CFCs, SF₆, and radiocarbon (¹⁴C) provide invaluable information about the timescales of ocean mixing and deep water formation.

Henry's Law & Gas Solubility

At equilibrium, the concentration of a dissolved gas is proportional to its partial pressure in the atmosphere above the liquid. Henry's law states:

$$p_{\text{gas}} = K_H \cdot C$$

where $p_{\text{gas}}$ is the partial pressure (atm), $K_H$ is the Henry's law constant, and $C$ is the dissolved concentration (mol/kg).

Equivalently, the equilibrium (saturation) concentration is:

$$C_{\text{sat}} = \frac{p_{\text{gas}}}{K_H} = K_0 \cdot p_{\text{gas}}$$

$K_0 = 1/K_H$ is the solubility coefficient. Solubility increases with decreasing temperature and decreasing salinity.

O₂

~200-350 mumol/kg at surface

Essential for aerobic life

N₂

~400-600 mumol/kg at surface

Largely biologically inert

CO₂

~10-25 mumol/kg at surface

Reactive: forms carbonate system

Temperature & Salinity Dependence

Gas solubility in seawater is parameterized using empirical fits. For oxygen, the Garcia & Gordon (1992) formulation uses a scaled temperature variable $T_s$:

$$\ln C_{\text{sat}} = A_0 + A_1 T_s + A_2 T_s^2 + A_3 T_s^3 + S(B_0 + B_1 T_s + B_2 T_s^2)$$

where $T_s = \ln\left(\frac{298.15 - T}{273.15 + T}\right)$ and$A_i, B_i$ are empirically determined coefficients.

Temperature Effect

Cold water dissolves more gas. O₂ saturation at 0 degrees C is ~350 mumol/kg but only ~200 mumol/kg at 30 degrees C. This is why polar waters are oxygen-rich and tropical surface waters can be near saturation despite lower absolute concentrations.

Salinity Effect (Salting Out)

Dissolved ions occupy space in the water structure and reduce the capacity for gas molecules. O₂ solubility decreases ~2% per PSU increase. Freshwater holds ~20% more O₂ than seawater at the same temperature.

Air-Sea Gas Exchange: Piston Velocity Model

The flux of gas across the air-sea interface is driven by the concentration difference between the actual dissolved concentration and the saturation value. The piston velocity (gas transfer velocity) $k$ parameterizes the rate of exchange:

$$F = k \cdot (C_{\text{sat}} - C)$$

$F$ = flux (mol m⁻² s⁻¹), $k$ = piston velocity (m/s), positive $F$ = ocean uptake

The piston velocity depends strongly on wind speed. The widely used Wanninkhof (1992) parameterization relates $k$ to the 10-meter wind speed $u_{10}$:

$$k = 0.31 \cdot u_{10}^2 \cdot \left(\frac{Sc}{660}\right)^{-1/2}$$

$Sc$ = Schmidt number (ratio of kinematic viscosity to gas diffusivity).$Sc = 660$ for CO₂ at 20 degrees C in seawater.

Low Wind ($u_{10} < 3$ m/s)

Molecular diffusion dominates. Very slow exchange. k ~ 1-5 cm/hr.

High Wind ($u_{10} > 10$ m/s)

Bubble injection and wave breaking enhance exchange. k ~ 20-50 cm/hr.

Derivation: Henry's Law from Thermodynamics

Step 1: Chemical Potential at Equilibrium

At air-sea equilibrium, the chemical potential of a gas must be equal in both phases. For gas species $i$ partitioned between the gas phase (g) and dissolved phase (aq):

$$\mu_i^{(\text{g})} = \mu_i^{(\text{aq})}$$

Step 2: Expressing Chemical Potentials

For an ideal gas, $\mu_i^{(\text{g})} = \mu_i^{0,\text{g}} + RT \ln p_i$. For the dissolved species, using the molality scale with activity coefficient $\gamma_i$:

$$\mu_i^{0,\text{g}} + RT \ln p_i = \mu_i^{0,\text{aq}} + RT \ln(\gamma_i m_i)$$

Step 3: Isolating the Concentration-Pressure Relationship

Rearranging and defining the standard free energy of dissolution$\Delta G_{\text{sol}}^0 = \mu_i^{0,\text{aq}} - \mu_i^{0,\text{g}}$:

$$RT \ln\frac{p_i}{\gamma_i m_i} = \Delta G_{\text{sol}}^0 \quad \Longrightarrow \quad \frac{p_i}{\gamma_i m_i} = \exp\left(\frac{\Delta G_{\text{sol}}^0}{RT}\right) \equiv K_H$$

Step 4: Henry's Law in the Dilute Limit

For dilute solutions where $\gamma_i \to 1$, this reduces to the familiar form. The solubility coefficient $K_0 = 1/K_H$ gives concentration per unit pressure:

$$p_i = K_H \cdot C_i \qquad \text{or equivalently} \qquad C_{\text{sat}} = K_0 \cdot p_i$$

Step 5: Temperature Dependence (van't Hoff)

The temperature dependence of $K_H$ follows from the enthalpy of dissolution$\Delta H_{\text{sol}}$. Integrating the van't Hoff equation between reference temperature $T^*$ and $T$:

$$\ln\frac{K_H(T)}{K_H(T^*)} = -\frac{\Delta H_{\text{sol}}}{R}\left(\frac{1}{T} - \frac{1}{T^*}\right)$$

Since dissolution of gases is exothermic ($\Delta H_{\text{sol}} < 0$),$K_H$ increases (solubility decreases) with temperature, explaining why cold water holds more gas.

Step 6: Salting-Out Effect (Setchenov Equation)

In electrolyte solutions, ions disrupt the water structure and reduce the solubility of neutral gas molecules. The Setchenov (Sechenov) equation accounts for this:

$$\ln\frac{K_H(S)}{K_H(0)} = k_s \cdot S \quad \Longrightarrow \quad \ln\gamma_{\text{gas}} = k_s \cdot S$$

where $k_s$ is the Setchenov coefficient (positive for salting-out). For O₂ in seawater, $k_s \approx 0.006$ per PSU, reducing solubility by ~20% at S = 35.

Derivation: Gas Transfer Velocity

Step 1: The Thin-Film (Stagnant Boundary Layer) Model

Near the air-sea interface, turbulent mixing is suppressed, and gas transport occurs by molecular diffusion across a thin boundary layer of thickness $\delta$. Fick's first law gives the flux:

$$F = D \frac{C_{\text{sat}} - C_{\text{bulk}}}{\delta} = k(C_{\text{sat}} - C)$$

where the piston velocity (gas transfer velocity) is identified as $k = D/\delta$, with $D$ the molecular diffusivity of the gas in water.

Step 2: Schmidt Number Scaling

The boundary layer thickness depends on the ratio of momentum diffusivity (kinematic viscosity $\nu$) to mass diffusivity ($D$). The Schmidt number captures this ratio:

$$Sc = \frac{\nu}{D}$$

Boundary layer theory predicts $\delta \propto Sc^n$, where $n = 1/2$ for a smooth surface (surface renewal model) or $n = 2/3$ for a rigid surface (film model).

Step 3: Wind Speed Dependence

Wind stress generates turbulence at the surface, thinning the boundary layer. Empirically,$k$ scales as $u_{10}^2$ at moderate to high wind speeds (consistent with a drag-law scaling where stress $\tau \propto u_{10}^2$). Combining:

$$k = a \cdot u_{10}^2 \cdot \left(\frac{Sc}{660}\right)^{-1/2}$$

Normalized to $Sc = 660$ (CO₂ at 20 degrees C). Wanninkhof (1992) determined $a = 0.31$using global bomb-¹⁴C inventories as a constraint on the globally averaged transfer velocity.

Step 4: Surface Renewal Model

An alternative to the thin-film model: turbulent eddies periodically bring fresh bulk water to the surface, where it equilibrates by diffusion for a characteristic time $\tau$before being replaced. The resulting transfer velocity is:

$$k = \sqrt{\frac{D}{\pi \tau}} \propto D^{1/2} \propto Sc^{-1/2}$$

This model naturally gives the $Sc^{-1/2}$ dependence observed in wind-tunnel experiments, supporting the Wanninkhof parameterization.

Step 5: Bubble-Mediated Transfer at High Winds

At wind speeds above ~10 m/s, breaking waves inject bubbles below the surface. Gas dissolves from pressurized bubbles, adding a flux component that is nearly independent of solubility:

$$F_{\text{total}} = k(C_{\text{sat}} - C) + F_{\text{bubble}} \quad \text{where} \quad F_{\text{bubble}} = b \cdot u_{10}^3 \cdot p_{\text{gas}} \cdot V_b$$

The cubic wind speed dependence for bubble injection enhances the transfer of less soluble gases (e.g., O₂, N₂) more than soluble ones (CO₂), creating supersaturation of N₂ and O₂ in storm conditions.

Derivation: Oxygen Saturation Concentration

Step 1: Starting from Henry's Law for O₂

The saturation concentration of O₂ in seawater at 1 atm total pressure is determined by the atmospheric O₂ mole fraction ($x_{\text{O}_2} = 0.20946$) and the Henry's law solubility:

$$C_{\text{sat}}^{\text{O}_2} = K_0^{\text{O}_2}(T, S) \cdot (P_{\text{atm}} - p_{\text{H}_2\text{O}}) \cdot x_{\text{O}_2}$$

where $p_{\text{H}_2\text{O}}$ is the water vapor pressure (subtracted because only dry gas contributes).

Step 2: Empirical Parameterization of K₀

Garcia and Gordon (1992) fit the solubility to a polynomial in the scaled temperature variable$T_s$, which compresses the temperature range for better polynomial behavior:

$$T_s = \ln\left(\frac{298.15 - T}{273.15 + T}\right)$$

This transformation maps the oceanographic temperature range (roughly -2 to 40 degrees C) onto a roughly linear scale, since $T_s$ is monotonically decreasing with temperature.

Step 3: Full Garcia-Gordon Formula

The natural log of the saturation concentration is expanded as a polynomial in $T_s$with salinity-dependent corrections:

$$\ln C_{\text{sat}} = A_0 + A_1 T_s + A_2 T_s^2 + A_3 T_s^3 + A_4 T_s^4 + A_5 T_s^5 + S(B_0 + B_1 T_s + B_2 T_s^2 + B_3 T_s^3) + C_0 S^2$$

Step 4: Physical Origin of Each Term

The polynomial structure arises from expanding the thermodynamic functions:

$$\ln K_0 = -\frac{\Delta G_{\text{sol}}^0}{RT} = -\frac{\Delta H_{\text{sol}}^0}{RT} + \frac{\Delta S_{\text{sol}}^0}{R} + \frac{\Delta C_p}{R}\left(\frac{T^*}{T} - 1 + \ln\frac{T}{T^*}\right) + \cdots$$

The leading terms ($A_0, A_1$) capture the enthalpy and entropy of dissolution. Higher-order terms ($A_2$ onward) account for the heat capacity change upon dissolution. The salinity terms ($B_i$) represent the salting-out effect from the Setchenov relation.

Step 5: Pressure Correction at Depth

For in-situ saturation at depth, the hydrostatic pressure increases the solubility via the partial molar volume of O₂ in solution $\bar{V}_{\text{O}_2}$:

$$\ln\frac{K_0(P)}{K_0(1\,\text{atm})} = \frac{\bar{V}_{\text{O}_2}(P - 1)}{RT}$$

With $\bar{V}_{\text{O}_2} \approx 32$ cm³/mol, the pressure correction increases solubility by roughly 1.4% per 1000 dbar, a small effect relevant mainly for deep water calculations.

Oxygen Minimum Zones & Apparent Oxygen Utilization

As organic matter sinks below the euphotic zone, microbial respiration consumes dissolved O₂. This creates oxygen minimum zones (OMZs) at intermediate depths (200-1000 m), where O₂ can fall below 20 mumol/kg. Major OMZs occur in the eastern tropical Pacific, Arabian Sea, and Bay of Bengal.

$$\text{AOU} = C_{\text{sat}}(T, S) - C_{\text{measured}}$$

Apparent Oxygen Utilization: the amount of O₂ consumed since the water was last in contact with the atmosphere. High AOU indicates old, respiration-rich water.

The Oxygen Budget

The rate of change of dissolved O₂ at any point in the ocean reflects the balance between physical supply (advection + diffusion + air-sea exchange) and biological consumption:

$$\frac{\partial [\text{O}_2]}{\partial t} = -\mathbf{u} \cdot \nabla [\text{O}_2] + K \nabla^2 [\text{O}_2] + J_{\text{bio}}$$

$J_{\text{bio}} > 0$ (production) in euphotic zone; $J_{\text{bio}} < 0$ (consumption) below

Biological Pump for Gases

Photosynthesis in the surface produces O₂ and consumes CO₂. Sinking organic matter exports this signal downward, where respiration reverses the reaction: deep waters accumulate CO₂ and lose O₂.

Expanding OMZs

Global warming reduces O₂ solubility and increases stratification, limiting ventilation. OMZs have expanded by 3-8% since the 1960s, threatening marine ecosystems and fisheries.

Noble Gas & Transient Tracers

Noble gases (He, Ne, Ar, Kr, Xe) are biologically inert and serve as tracers for physical processes. Their solubilities vary with temperature, allowing reconstruction of water mass formation temperatures. Helium-3 excess from hydrothermal vents traces deep ocean circulation.

CFC Tracers

Chlorofluorocarbons (CFC-11, CFC-12) were released industrially since the 1930s. Their atmospheric history is well known, so measuring CFCs in deep water constrains the time since that water was last at the surface. CFC-12 ages range from 0 (surface) to ~60 years.

Radiocarbon (¹⁴C)

¹⁴C decays with a half-life of 5730 years. The ratio $\Delta^{14}\text{C}$ in dissolved inorganic carbon reveals water mass ages from decades to millennia. The oldest deep Pacific water has $\Delta^{14}\text{C} \approx -240$ per mille (~2000 years).

Argon/Oxygen Ratios

Since Ar is biologically inert but has similar solubility to O₂, the O₂/Ar ratio separates biological O₂ production from physical effects (temperature, bubbles). This enables measurement of net community production directly from dissolved gas measurements.

Python: Gas Solubility, Air-Sea CO₂ Flux & AOU

Compute O₂ solubility curves, air-sea CO₂ flux with wind dependence, and AOU profiles:

Python: Gas Solubility, Air-Sea CO₂ Flux & AOU

Python

!/usr/bin/env python3

script.py75 lines

Click Run to execute the Python code

Code will be executed with Python 3 on the server

Fortran: Air-Sea Gas Exchange Model

This Fortran program simulates time-dependent air-sea gas exchange for CO₂ with wind speed dependence, tracking mixed-layer DIC evolution over 10 years:

Fortran: Air-Sea Gas Exchange Model

Fortran

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program.f9069 lines

Click Run to execute the Fortran code

Code will be compiled with gfortran and executed on the server

Key Takeaways

  • Gas solubility follows Henry's law and increases with decreasing temperature and salinity.
  • Air-sea gas flux $F = k(C_{\text{sat}} - C)$ is controlled by wind speed through the piston velocity.
  • Oxygen minimum zones result from the balance between respiration and ventilation at intermediate depths.
  • AOU measures the integrated oxygen consumption since a water parcel left the surface.
  • Transient tracers (CFCs, ¹⁴C, noble gases) constrain ocean ventilation ages and circulation pathways.