Bioreactor Oxygen Transfer: kLa, OTR and Max Cell Density

Calculate oxygen solubility, kLa, OTR, oxygen demand and dry biomass limits. Compare oxygen capacity with jacket cooling duty and explore an animated dissolved-oxygen transient.

#biomass #bioreactor #gassing-out #jacket cooling #kLa #OUR #oxygen transfer #van 't Riet

This oxygen transfer rate calculator connects the gas supply, dissolved oxygen, culture demand and cooling duty of a stirred bioreactor. It is intended for bioprocess engineers, students and laboratory teams comparing operating conditions before a cultivation or scale-up study. Results are expressed as dry biomass concentration, so they can be used with a measured specific oxygen uptake rate without assuming a mass per cell.

Start with the broth temperature, absolute gas pressure and dry-gas oxygen fraction. Air contains about 0.2095 oxygen by mole; an enriched mixture increases the equilibrium dissolved concentration. The water-solubility model includes temperature and water-vapor pressure. Enter a broth-to-water correction when you have medium measurements. The illustrative default correction is 0.95; salts, proteins and other ingredients may require a different value.

For a kLa calculation for a bioreactor, choose one of the two van 't Riet correlations or the gassing-out option. The correlations use gassed mechanical power per liquid volume and superficial gas velocity. Coalescing and non-coalescing liquids can behave differently, and neither selection replaces characterization of a real broth. In gassing-out mode, enter two rising DO readings as fractions of the final equilibrium value and the time between them. Use a cell-free test at the intended operating conditions with a sufficiently fast probe. The logarithmic two-point estimate does not provide the statistical diagnostics of a full regression.

Next enter the minimum acceptable DO, the specific uptake per gram of dry biomass, and the operating biomass concentration. Here the minimum DO is relative to equilibrium with the selected gas mixture and pressure. Convert an air-calibrated sensor setpoint if necessary. The calculator compares bioreactor oxygen demand with transfer capacity at that minimum DO. Their intersection defines an oxygen-limited biomass ceiling, while the required-kLa result shows the transfer coefficient needed at the operating biomass.

Heat removal is evaluated separately. Oxygen uptake produces estimated metabolic heat, and dissipated stirring power adds to the required jacket duty. Enter the working volume, available jacket UA and mean broth-to-coolant temperature difference. The combined biomass ceiling is the lower of the oxygen and cooling ceilings. It is a capacity estimate, not a prediction of growth or productivity.

Press play to follow an illustrative dissolved-oxygen response with constant uptake. The animated bubbles represent aeration; the trace shows how transfer and demand compete. No DO controller, gas depletion, oxygen feed-flow limit, shear constraint or biological inhibition is simulated. If the trace reaches zero, fixed uptake is no longer physiologically sustainable. Use measured kLa, uptake, solubility and heat-transfer data to refine a process design.

How it is calculated

The liquid oxygen balance is dC/dt=kLa(C∗−C)−OURdC/dt=k_La(C^*-C)-OUR, with OUR=qO2XOUR=q_{O2}X.

Solubility. Freshwater air saturation follows the Benson–Krause polynomial in USGS Technical Memorandum 2011.03, attached file page 6, equation 7. The same page, equation 11, gives water vapor pressure. The tool scales by the dry-gas pressure ratio (p−pv)/(101.325−pv)(p-p_v)/(101.325-p_v), oxygen mole fraction relative to 0.2095, and the user-entered broth/water solubility ratio. This uses ideal Henry-law pressure scaling and omits the small near-atmospheric virial correction in USGS equation 9.

Transfer. Van 't Riet (1979), DOI 10.1021/i260071a001, gives the customary coalescing kLa=0.026(Pg/V)0.4ug0.5k_La=0.026(P_g/V)^{0.4}u_g^{0.5} and non-coalescing kLa=0.002(Pg/V)0.7ug0.2k_La=0.002(P_g/V)^{0.7}u_g^{0.2} forms, with SI numerical inputs W/m³ and m/s and output s⁻¹. The coefficients are also documented in the attached DECHEMA 2020 recommendations, page 17, equations 9–10. Normalization quantities in the steps make those dimensional empirical coefficients explicit. No automatic viscosity or temperature correction is applied to kLa.

The alternative cell-free gassing-out estimate is the two-point logarithmic slope kLa=ln⁡[(1−f1)/(1−f2)]/Δtk_La=\ln[(1-f_1)/(1-f_2)]/\Delta t. Fractions refer to the final measured equilibrium in that test. The default 0.2 and 0.8 endpoints span the usual 20–80% range. It is not a multipoint statistical regression. The independent reference cases use measured endpoints from DECHEMA 2020, attached page 55, and compare with published regression slopes on page 56; this simplified estimate is not an implementation of the complete DECHEMA measurement protocol.

Capacity and heat. OTR=kLa(C∗−Cmin)OTR=k_La(C^*-C_{min}) and XO2=OTR/qO2X_{O2}=OTR/q_{O2}. Metabolic heat is oxygen uptake times the positive oxycaloric equivalent. The 460 kJ/mol default is an estimate; Luong and Volesky (1980), DOI 10.1002/cjce.5450580412, report 465 kJ/mol for rates and 461 kJ/mol for totals. Required jacket duty adds gassed stirring power. Available heat removal is UAΔTmeanUA\Delta T_{mean}. Cooling biomass capacity uses the heat removal remaining after stirring, clamped to zero. The combined ceiling is the lower of the oxygen and cooling ceilings.

The transient is the closed-form, constant-OUR solution, clipped at zero oxygen. Its trace spans five transfer time constants, capped at two hours. Bubble motion illustrates aeration and is not a predicted bubble trajectory.

Assumptions

  • Uniform, well-mixed liquid; constant working volume, temperature, effective pressure, effective dry-gas composition, kLa and specific uptake.
  • Biomass is dry mass per liquid volume, not cells/mL. Enter strain-specific uptake per gram dry mass; no cell mass conversion is assumed.
  • The minimum DO is a fraction of equilibrium under the selected operating conditions. A sensor calibrated to air saturation may require conversion before use.
  • The broth/water solubility ratio and default uptake are illustrative user assumptions. Non-coalescing kLa does not itself correct oxygen solubility for salts.
  • All gassed mechanical power becomes broth heat. Feed, evaporation, wall losses and other heat sources are omitted.
  • Jacket UA and mean driving temperature difference are supplied by the user. Coolant flow and warming are represented only through these values.

Where it applies

Use for screening nonviscous, sparged stirred tanks and teaching the coupled oxygen/heat balances. Freshwater solubility is restricted to 0–40 °C. USGS documents near-atmospheric solubility methods at about 0.5–1.1 atm; extension to 3 bar absolute and oxygen enrichment uses ideal partial-pressure scaling, not a validated high-pressure broth model.

Van 't Riet correlations describe conventional low-viscosity gas–liquid systems; real broths, antifoam, impellers, spargers, flooding, shear limits and scale can change kLa substantially. The 500–10,000 W/m³ advisory band is a screening guard, not proof that a vessel is within a correlation's domain. Prefer measurements in the intended broth and operating range.

Gassing-out requires no oxygen-consuming cells or reactions, constant operating conditions, a stable equilibrium reading and negligible probe delay. A two-point fit has no confidence interval or diagnostic residuals.

The reported ceilings assume sufficient feed-gas oxygen and a representative gas composition. Gas-phase depletion, oxygen supply flow limits, hydrostatic gradients, non-Newtonian mixing, substrate limitations and biological inhibition are not solved. Do not infer a growth forecast or guaranteed achievable density. The constant-OUR transient ceases to describe cell physiology after oxygen depletion; the zero plateau only marks that boundary. Fermentative or mixed metabolism can invalidate the heat/oxygen estimate.

References

  • Van 't Riet, K. (1979). Review of measuring methods and results in nonviscous gas–liquid mass transfer in stirred vessels. Ind. Eng. Chem. Process Des. Dev. 18, 357–364. https://doi.org/10.1021/i260071a001
  • Garcia-Ochoa, F. and Gomez, E. (2009). Bioreactor scale-up and oxygen transfer rate in microbial processes: an overview. Biotechnology Advances 27, 153–176. https://doi.org/10.1016/j.biotechadv.2008.10.006
  • Luong, J.H.T. and Volesky, B. (1980). Determination of the heat of some aerobic fermentations. Canadian Journal of Chemical Engineering 58, 497–504. https://doi.org/10.1002/cjce.5450580412
  • USGS (2011). Office of Water Quality Technical Memorandum 2011.03, attached page 6, equations 7 and 11. https://water.usgs.gov/water-resources/memos/documents/WQ.2011.03.pdf
  • Shelton, L.R. (1994). USGS Open-File Report 94-455, Table 4: independent, rounded Weiss-based oxygen-solubility values used for reference checks. https://water.usgs.gov/nawqa/pnsp/pubs/ofr94-455/sw-t.html
  • DECHEMA (2020). Recommendations for process engineering characterisation of single-use bioreactors and mixing systems by using experimental methods, 2nd edition. Attached p. 17 (correlations), pp. 50 and 55–56 (gassing-out method and measured example). https://dechema.de/dechema_media/Downloads/Positionspapiere/Single_Use_BioReactors_2020-p-20006899.pdf

Inputs

InputSymbolUnitDefault
kLa method
Correlations are screening estimates for nonviscous stirred tanks. Use a measured fit for your broth.
kla_modeVan 't Riet — coalescing liquid
Broth temperatureT_b°C30
Effective absolute gas pressure
Absolute, not gauge. Use a representative bubble pressure; the model does not calculate hydrostatic pressure.
p_abskPa101.325
Effective dry-gas O₂ mole fraction
Air = 0.2095. Use a representative gas composition when oxygen depletion is appreciable.
y_O20.2095
Broth / water solubility ratio
Measured medium correction; 1 is fresh water. The default 0.95 is illustrative, not a universal broth property.
beta_b0.95
Gassed mechanical power per liquid volume
Actual mechanical power dissipated in aerated broth, not motor nameplate power. Also included in cooling duty.
P_VW/m^31000
Superficial gas velocity
Actual gas volumetric flow at vessel conditions divided by vessel cross-sectional area.
u_gm/s0.005
First DO / final equilibrium DOf_10.2
Second DO / final equilibrium DOf_20.8
Time between DO readings
Cell-free reoxygenation at constant operating conditions. Use a probe much faster than the transfer response.
dt_fits50
Minimum DO / operating equilibrium DO
0.30 means 30% of equilibrium at the selected temperature, pressure, gas and broth correction; it is not always 30% air saturation.
f_DO0.3
Specific oxygen uptake per dry biomass
Enter a measured rate for your strain, substrate and growth state. Default is illustrative.
q_O2mmol/(g*h)5
Operating dry biomass concentrationX_bg/L2
Working liquid volumeV_LL100
Heat released per oxygen consumed
460 is an aerobic screening estimate. Luong and Volesky (1980) report 465 kJ/mol from rate data and 461 kJ/mol from totals.
H_O2kJ/mol460
Available jacket conductance, UA
Use the fouled operating conductance from equipment data; no jacket-area correlation is assumed.
UA_jW/K50
Broth-to-coolant mean temperature difference
Use the log-mean difference if coolant warms along the jacket.
DT_jK15
Initial DO / operating equilibrium DO
Illustrative reoxygenation with constant biomass and OUR. The DO controller is not simulated.
f_init0.1
Elapsed time ▶t_anims30

Results

With the default inputs above, the calc gives:

ResultValue
Selected kLa104.896 h⁻¹
Operating oxygen solubility7.181 mg/L
OTR capacity at minimum DO16.478 mmol/(L·h)
Operating oxygen demand10 mmol/(L·h)
Oxygen biomass ceiling3.296 g/L
Cooling biomass ceiling10.174 g/L
Combined dry biomass ceiling3.296 g/L
Required jacket duty227.778 W
Available jacket duty750 W
kLa required at operating biomass63.657 h⁻¹

Checked against sources

Each case below was calculated by this calc and agrees with the value from its source (within the tolerance where one is shown).

USGS Table 4 — fresh water at 0 °C and 760 mmHg

Source: Shelton (1994), USGS OFR 94-455, Table 4, 0.0 °C / 760 mmHg = 14.6 mg/L. https://water.usgs.gov/nawqa/pnsp/pubs/ofr94-455/sw-t.html . Independent rounded Weiss-based table; 0.05 mg/L tolerance allows table rounding and the documented small Weiss/Benson–Krause difference.

Inputs: Broth temperature = 0 °C; Broth / water solubility ratio = 1; Operating dry biomass concentration = 0 g/L; the others as above.

ResultSourceThis calc
Operating oxygen solubility14.6 ± 0.05 mg/L14.621 mg/L

USGS Table 4 — fresh water at 20 °C and 760 mmHg

Source: Shelton (1994), USGS OFR 94-455, Table 4, 20.0 °C / 760 mmHg = 9.1 mg/L. https://water.usgs.gov/nawqa/pnsp/pubs/ofr94-455/sw-t.html . Independent published rounded Weiss-based table; tolerance is 0.05 mg/L, not a fitted coefficient.

Inputs: Broth temperature = 20 °C; Broth / water solubility ratio = 1; Operating dry biomass concentration = 0 g/L; the others as above.

ResultSourceThis calc
Operating oxygen solubility9.1 ± 0.05 mg/L9.092 mg/L

USGS Table 4 — fresh water at 20 °C and 600 mmHg

Source: Shelton (1994), USGS OFR 94-455, Table 4, 20.0 °C / 600 mmHg = 7.1 mg/L. https://water.usgs.gov/nawqa/pnsp/pubs/ofr94-455/sw-t.html . Independent published pressure point; 600/760 × 101.325 kPa. Tolerance accommodates table rounding and the older solubility formulation.

Inputs: Broth temperature = 20 °C; Broth / water solubility ratio = 1; Effective absolute gas pressure = 79.993 kPa; Operating dry biomass concentration = 0 g/L; the others as above.

ResultSourceThis calc
Operating oxygen solubility7.1 ± 0.05 mg/L7.133 mg/L

DECHEMA measured gassing-out data — run 1

Source: DECHEMA 2020, attached pp. 55–56, Table 6 and Figure 13. Run 1: DO 27.35% at 0.0111 h and 80.03% at 0.0389 h, final DO*=100%. Independent published regression slope 46.25 h⁻¹. The calculator uses two measured endpoints, not the full regression; tolerance 0.6 h⁻¹ (1.3%) allows that distinction and rounded measurement times. https://dechema.de/dechema_media/Downloads/Positionspapiere/Single_Use_BioReactors_2020-p-20006899.pdf

Inputs: kLa method = Gassing-out — two-point log fit; Broth temperature = 37 °C; Working liquid volume = 2 L; First DO / final equilibrium DO = 0.2735; Second DO / final equilibrium DO = 0.8003; Time between DO readings = 100.1 s; Operating dry biomass concentration = 0 g/L; the others as above.

ResultSourceThis calc
Selected kLa46.25 ± 0.6 h⁻¹46.454 h⁻¹

DECHEMA measured gassing-out data — run 2

Source: DECHEMA 2020, attached pp. 55–56, Table 6 and Figure 13. Run 2: DO 30.11% at 0.0111 h and 80.69% at 0.0389 h, final DO*=100%. Independent published regression slope 46.14 h⁻¹; a 0.6 h⁻¹ tolerance allows two-endpoint versus full-regression estimation and measurement rounding. https://dechema.de/dechema_media/Downloads/Positionspapiere/Single_Use_BioReactors_2020-p-20006899.pdf

Inputs: kLa method = Gassing-out — two-point log fit; Broth temperature = 37 °C; Working liquid volume = 2 L; First DO / final equilibrium DO = 0.3011; Second DO / final equilibrium DO = 0.8069; Time between DO readings = 100.1 s; Operating dry biomass concentration = 0 g/L; the others as above.

ResultSourceThis calc
Selected kLa46.14 ± 0.6 h⁻¹46.27 h⁻¹

Related Resources

Responses

Your email address will not be published. Required fields are marked *

L ading...