Separate suspended load from catchment erosion
Trace sediment production, transport and storage without attributing an outlet total to an unmeasured source.
Learning outcome: State what a gauge load measures and identify additional evidence needed for erosion or intervention claims.
Starting recap
Weathering alters material in place; erosion removes it; transport moves it and deposition stores it. Outlet suspended load captures only part of that history.
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Try
A 151.2-tonne suspended load at the modeled gauge does not show that 151.2 tonnes of new hillslope erosion occurred during the six-hour event.
Open the experimentPredict
Can two catchments deliver the same outlet suspended load while having different erosion and storage histories?
Experiment
Compare the aligned and late schedules and state the measured-section quantity each total represents. Draw alternative upstream source-and-storage histories consistent with one total.
Integrate a storm suspended-sediment load
Worked teaching model · synthetic values · Six fictional one-hour intervals with constant values within each interval. Base streamflow is 10, 20, 40, 40, 20, 10 m³/s. Concentration is assumed representative of the whole flowing cross-section, not a point sample or turbidity reading. Changing timing rearranges the same six concentration values. Flow scaling holds concentration fixed as a controlled accounting exercise, not a causal runoff or erosion model. The paired sum is exact only for these supplied piecewise-constant records; bedload and dissolved material are excluded.
Reset keeps your prediction, captures and practice history.
| Hours | Q (m³/s) | C (mg/L) | Rate (kg/s) | Hour mass (kg) | Cumulative (kg) |
|---|---|---|---|---|---|
| 0–1 | 10 | 100 | 1.00 | 3,600 | 3,600 |
| 1–2 | 20 | 200 | 4.00 | 14,400 | 18,000 |
| 2–3 | 40 | 400 | 16.00 | 57,600 | 75,600 |
| 3–4 | 40 | 400 | 16.00 | 57,600 | 133,200 |
| 4–5 | 20 | 200 | 4.00 | 14,400 | 147,600 |
| 5–6 | 10 | 100 | 1.00 | 3,600 | 151,200 |
| Method | Mass (kg) | Error: estimate minus paired sum (kg) | Relative error (%) |
|---|---|---|---|
| Paired hourly integration | 151,200 | 0 | 0.00 |
| Product of separate time means | 117,600 | -33,600 | -22.22 |
| First-bin concentration for all water | 50,400 | -100,800 | -66.67 |
Time-mean Q: 23.333 m³/s; time-mean C: 233.333 mg/L. Water volume: 504,000 m³. Flow-weighted C: 300.000 mg/L. Equal separate means do not preserve the time pairing needed for load. A shortcut that matches one case can still be unreliable in another.
These are fictional interval records, not storm measurements. A section's suspended load omits bedload and dissolved material and cannot locate sediment sources or separate fresh erosion from remobilized storage. Real sampling must address timing and cross-section representativeness.
Six-hour suspended mass: 151,200 kg (151.2 metric tonnes). Water volume: 504,000 m³.
Rate = Q × C × 0.001 kg/s; each hourly mass is rate × 3,600 s. Flow-weighted concentration = 300.00 mg/L; separate time-mean concentration = 233.33 mg/L. Suspended mass at this section is not whole-watershed gross erosion.
Captures preserve recipes and replay their calculated results. They are synthetic model evidence, not physical measurements.
Understand
Apply
Public practice checks a specific claim. It does not establish independent mastery.
Separate suspended load from bedload and dissolved transport, name unmeasured storage changes, and explain what evidence would be needed to assess a vegetation intervention.
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