Example preset
Choose a preset to fill the form and refresh results instantly.
Quick check
Pick one tab first: DO, load, or removal rate.
Check units for pressure, concentration, and flow.
Run with sample values before entering field data.
Keep source notes when you export values.
Inputs
Advanced settings
Count backwards (optional)
Results
| DOSaturation concentration | — |
|---|---|
| % saturation | — |
| Shortage amount (saturation - measurement) | — |
| condition | — |
| u(atm) | — |
|---|---|
| θo | — |
| FS | — |
| FP | — |
| Load amount within the period | — |
|---|---|
| Converted per day | — |
| period volume V | — |
| Midway ceremony | — |
| Removal rate R | — |
|---|---|
| Cout_target from target removal rate | — |
| Required removal rate from target Cout | — |
Premise/Source/Caution
- The DO formula adopts the USGS Office of Water Quality Technical Memorandum 2011.03 (Benson & Krause approximation formula).
- The recommended range for DO is 0~40℃, 0~40‰, 0.5~1.1 atm (approximately 507~1114 hPa). Calculation continues even outside the range.
- BOD/COD loads are estimates based on the basic formula: C x Q x Time (1 mg/L = 1 g/m³). Reaction, precipitation, and adsorption are not considered.
- Please do not use it for regulatory judgments or design guarantees, but only for learning and initial estimates.
Reference: USGS WQ 2011.03 / Benson & Krause (1984)
How to use this calculator effectively
This guide helps you use DO saturation and BOD/COD calculator in a repeatable way: define a baseline, change one variable at a time, and explain each output using explicit assumptions before sharing results.
How it works
The calculator applies deterministic formulas to your input values and only rounds at the final display layer. This makes it useful for comparative analysis: keep one scenario as a baseline, then vary assumptions and measure the delta in both absolute terms and percentage terms. If a change appears too large or too small, verify units, period conventions, and sign direction before interpreting the result.
When to use
Use this page when you need a fast planning estimate, a classroom check, or a reproducible scenario that teammates can review. It is most effective at the decision-prep stage, where you need to compare options quickly and decide which assumptions deserve deeper modeling or external validation.
Common mistakes to avoid
- Mixing units such as percent vs decimal, or monthly vs yearly settings.
- Changing multiple fields at once, which hides the real cause of result movement.
- Comparing outputs across tools without aligning constants and default conventions.
- Treating rounded display values as exact inputs for downstream calculations.
Interpretation and worked example
Start with a baseline case and save that output. Next, edit one assumption to reflect your realistic alternative, then compare both the direction and size of change. If the direction matches domain intuition and magnitude is plausible, your setup is likely coherent. If not, check hidden defaults, unit conversions, boundary conditions, and date logic before drawing conclusions.
See also
- Atmospheric pressure ↔ Altitude (standard atmosphere/sea level correction) (ES-003)
- Nutrient load (N/P): Concentration x flow rate x time → load amount (ES-010)
- Open channel (Manning type) flow rate/flow rate (rectangular/trapezoidal/circular) (ES-013)
- Rainfall (mm) → Volume (m³)/Flow rate (m³/s) conversion (ES-004)
FAQ
What should I enter first?
Start with the minimum required inputs shown above the calculate button, then keep optional settings at their defaults for a first pass. After getting a baseline, change one parameter at a time so you can explain which assumption moved the output.
How precise are the results?
The calculator keeps internal precision and rounds only for display. Small differences can still appear if another tool uses different constants, period conventions, or rounding rules. Align assumptions before comparing final values.
Why can my result differ from another calculator?
Many tools choose different defaults for units, rate basis, date-count logic, and sign conventions. Verify those defaults first. If differences remain, use the worked example and compare each intermediate step to locate the branch that diverges.
Can I use this output for official decisions?
Use this page for educational planning and quick checks. For legal, medical, tax, or regulated decisions, confirm your result with official guidance or a qualified professional because institutional rules may include extra constraints.
Does this page send my inputs to a server?
Core calculations run in your browser. Some share links encode parameters in the URL so results can be reproduced, but no hidden upload is triggered unless you explicitly share that URL.
How to use DO saturation and BOD/COD calculator effectively
What this calculator does
This page is for estimating outcomes by changing inputs in one controlled workflow. The model keeps your focus on variables, not output shape. Start with stable assumptions, then test sensitivity by changing one key input at a time to observe directional impact.
Input meaning and unit policy
Each input has an expected unit and a typical range. For reliable interpretation, check whether you are using the same unit system, period, and base assumptions across all runs. Unit mismatch is the most common source of unexpected drift in numeric results.
Use-case sequence
A practical sequence is: first run with defaults, then create a baseline log, then run one alternative scenario, and finally compare only the changed output metric. This sequence reduces cognitive load and prevents false pattern recognition in early experiments.
Common mistakes to avoid
Avoid changing too many variables at once, mixing incompatible data sources, and interpreting a one-time output without checking robustness. A single contradictory input can flip conclusions, so keep each experiment minimal and document assumptions as part of your note.
Interpretation guidance
Review both magnitude and direction. Direction tells you whether a strategy moves outcomes in the desired direction, while magnitude helps you judge practicality. If both agree, you can proceed; if not, rebuild the baseline and verify constraints before deciding.
Related tools
- Geology/Environment (Water (Rain/Flow rate/Water quality))
- Atmospheric pressure ↔ Altitude (standard atmosphere/sea level correction) (ES-003)
- Nutrient load (N/P): Concentration x flow rate x time → load amount (ES-010)
- Open channel (Manning type) flow rate/flow rate (rectangular/trapezoidal/circular) (ES-013)
- Rainfall (mm) → Volume (m³)/Flow rate (m³/s) conversion (ES-004)