Dissolved O₂ Saturation Calculator

Calculate dissolved oxygen saturation at given temperature, salinity, and altitude using the USGS Benson & Krause (1984) standard. Compare measured DO to saturation with species-specific thresholds.

Aquatic Facility ScienceDO satClient-Side
Tool details, related tools, and citation

Try it out

Load example dissolved oxygen data to see the full workflow

Water Conditions

Results

DO Saturation
8.26
mg/L (theoretical max)
Barometric Pressure
101.33
kPa

Species Reference Ranges

SpeciesMinimum (mg/L)Optimal (mg/L)Status
Zebrafish468Above Optimal
General freshwater fish56.59Optimal
Coldwater (trout/salmon)6812Optimal
Marine tropical568Above Optimal

DO Saturation vs Temperature

Freshwater (S=0) Brackish (S=15) Seawater (S=35) Current
  • Determining expected DO saturation at your facility conditions
  • Comparing measured DO against the theoretical maximum
  • Assessing whether DO levels are adequate for your species
  • Evaluating the impact of altitude on oxygen availability

Don't use for

  • As a substitute for direct DO measurement — always use a calibrated DO probe
  • For real-time monitoring — this is a point calculation, not a continuous monitor
  • To predict DO in systems with active oxygen consumption — this calculates equilibrium saturation only

Benson & Krause (1984) Standard

The Benson & Krause equation is the USGS standard for calculating dissolved oxygen saturation in water:

ln(DO) = −139.34411 + (1.575701×10510^{5}/Tₖ) − (6.642308×10710^{7}/Tₖ²) + (1.2438×101010^{10}/Tₖ³) − (8.621949×101110^{11}/Tₖ⁴)

Where Tₖ = temperature in Kelvin. Salinity correction subtracts a salt-dependent term. Altitude correction scales by the ratio of local to sea-level atmospheric pressure.

This formula is accurate to ±0.01 mg/L across 0–40°C and 0–40 ppt salinity, making it the definitive reference for aquatic facility management.

Oxygen in Aquatic Biology

Dissolved oxygen is arguably the most critical water quality parameter:

  • Aerobic respiration: Fish extract O₂ via gills; inadequate DO causes respiratory distress and suffocation
  • Nitrification: Biofilter bacteria require >2 mg/L DO to convert ammonia to nitrate
  • Redox chemistry: Low DO shifts the redox balance, potentially releasing hydrogen sulfide from substrate
  • Behavioral indicator: Fish gasping at the surface ("piping") is an emergency sign of low DO

In recirculating systems, DO is consumed by fish, bacteria, and organic decay. Aeration (air stones, venturis, packed columns) must exceed the total oxygen demand.

Frequently Asked Questions