Trap-efficiency check for an existing sediment basin: Camp's equation, back-solved
A common scenario: the basin geometry comes from a prior project with similar drainage area. The reviewer wants the trap-efficiency calc before submittal. Given As and Q, back-solve Camp's equation for the capture particle, then run the 7-bin Stokes/Camp to get the weighted trap efficiency.
What you have
The basin geometry and design hydrology are fixed (someone else did the prior work). Your job is to verify it before submitting:
| Parameter | Value | Source |
|---|---|---|
| Surface area, As | 18,000 ft² | Existing geometry |
| Sediment storage volume | 12,000 ft³ | Below permanent pool |
| Drainage area | 6.0 ac | Disturbed |
| Design storm | 10-yr, 24-hr | NCDEQ standard |
| Design peak inflow, Q | 14 cfs | TR-55, computed separately |
| Soil texture | silt loam | SSURGO Web Soil Survey |
| Influent PSD | silt-loam reference | NRCS texture triangle |
Step 1 — Surface overflow rate
The fundamental Camp equation: a particle is captured if its settling velocity vs exceeds the surface overflow rate Q/As:
Convert to SI for the Stokes solve:
Step 2 — Back-solve Stokes for the capture particle
Stokes' law for spherical sediment in 20°C water, ρs = 2650 kg/m³, ρ = 1000, μ = 0.001 Pa·s:
Solve for d:
Apply Camp's 1.2 short-circuiting factor (real basins don't behave like ideal plug flow):
The basin captures 100% of all particles ≥ 0.0148 mm. That's finer than NCDEQ's 0.020 mm standard criterion — a good sign for design particle, but not the whole story.
Step 3 — 7-bin trap efficiency on a silt-loam PSD
The single design particle isn't the answer; you need the weighted efficiency across the full grain-size distribution. With As/Q = 1,285.7 (s/ft × 1):
| Bin | d (mm) | vs (ft/s) | % of yield | ηi | Trapped fraction |
|---|---|---|---|---|---|
| 1 (sand) | 0.500 | 2.30 × 10⁻¹ | 8% | ≫ 1 | 100% |
| 2 (very fine sand) | 0.100 | 2.95 × 10⁻² | 12% | 38 | 100% |
| 3 (coarse silt) | 0.050 | 7.38 × 10⁻³ | 18% | 9.5 | 100% |
| 4 (medium silt) | 0.020 | 1.18 × 10⁻³ | 22% | 1.52 | 100% |
| 5 (fine silt) | 0.010 | 2.95 × 10⁻⁴ | 15% | 0.379 | 37.9% |
| 6 (very fine silt) | 0.005 | 7.38 × 10⁻⁵ | 12% | 0.0949 | 9.5% |
| 7 (clay) | 0.002 | 1.18 × 10⁻⁵ | 13% | 0.0152 | 1.5% |
| Weighted trap efficiency | 100% | 67.0% | |||
Sum: 60% (bins 1-4) + 5.69% (bin 5) + 1.14% (bin 6) + 0.20% (bin 7) = 67.0%.
Step 4 — Closing the gap to 80%
To reach 80% trap efficiency on this silt-loam influent, you have to capture more of the fine-silt fraction. The basin already captures 100% of bins 1–4; the deficit lives entirely in bins 5–7.
| Option | Mechanism | Resulting η |
|---|---|---|
| PAM dosing at 5 ppm | Flocculates fine silt and clay into ~0.05 mm aggregates; bins 5–7 effectively captured | ~95% |
| Increase As to 36,000 ft² (2× larger) | η5 rises 38% → 76%; bins 6–7 still pass through; net rises modestly | ~75% |
| Increase As to 72,000 ft² (4× larger) | Sized for the 0.010 mm bin; bin 5 now 100% captured, bin 6 partial | ~83% |
| Add a 12% forebay (cleanout zoning) | Concentrates coarse for easy maintenance — does not meaningfully raise η; both cells see the same Q so coarse the forebay catches was going to be caught anyway. See the worked counter-example. | ~67% (no change) |
Recommendation: PAM dosing is the cheapest and most reliable option for this basin. If the project doesn't allow chemical addition, the only path to 80% is a 4× larger main basin — which often forces a re-layout of the site.
What changes if you tweak the inputs
| If you change… | The result moves… |
|---|---|
| Q = 14 → 22 cfs (25-yr storm) | Capture particle moves coarser to 0.0186 mm; trap efficiency drops to 60.5% |
| Soil silt loam → sandy loam (more sand in PSD) | Higher % in bins 1-3; trap efficiency rises to ~78% with same basin |
| As = 18,000 → 27,000 ft² (50% larger) | Q/As drops; capture particle 0.0148 → 0.0121 mm; η rises to ~72% |
| Add forebay (12% main As) | System η rises ~16 percentage points from forebay capture of bins 1–3 alone |
Run the back-solve in HydroComplete
Drop in any A_s and Q — get capture particle, full 7-bin trap efficiency, and the forebay/PAM what-if in one screen.
Sources and further reading
- Camp, T. R. (1946). Sedimentation and the Design of Settling Tanks. ASCE Transactions 111: 895-958.
- Stokes, G. G. (1851). On the effect of the internal friction of fluids on the motion of pendulums.
- NCDEQ. NC Erosion and Sediment Control Planning and Design Manual. §6.61 (Sediment Basins).
- EPA. Storm Water Management for Construction Activities. EPA-832-R-92-005.
— Michael Flynn, PE
When the basin geometry is fixed, the design problem becomes "what does this actually catch." Camp's equation runs both directions; the second direction is the one the reviewer asks about.
Related worked examples
- Sediment basin sizing for a 5-acre residential subdivision in Mecklenburg County, NCFull RUSLE → Camp's → 7-bin Stokes/Camp pipeline on a Charlotte residential subdivision. Comes out at 65.5% trap efficiency — below NCDEQ's 80%, so the example walks through forebay/PAM/upsizing remediation.
- RUSLE soil loss with cover-factor comparison on a 1-acre Asheville construction siteSame 1-acre Asheville site solved four times: bare grading, straw mulch, erosion blanket, temporary seed. Shows where the C-factor row in the RUSLE table actually moves the needle.
- Does a forebay improve trap efficiency? A worked counter-exampleA widely-repeated rule says forebays raise trap efficiency. The math says otherwise: 65.5% → 66.0% with 10% forebay, → 67.0% with 40% forebay. Forebays do other useful things — but they're not a capture-rate fix.
- PAM (polyacrylamide) in a sediment basin: from 65% to 92% trap efficiencySame 5-acre basin from scenario 1. With 5 ppm anionic PAM dosed at the inflow, the 7-bin trap efficiency moves from 65.5% to ~92% — without enlarging the basin. Dosing rate, application methods, cost, and the NPDES turbidity story.
- Detention pond routing to the pre-development peak: a 10-acre commercial site in Wake County, NCSCS runoff for pre and post conditions (14 cfs vs 41 cfs), TR-55 storage estimate, a two-stage outlet, and a full Modified Puls route that brings the 10-yr peak back under the allowable release. Every formula and number shown.
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