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Primary Tanks - PS208 Design Standards ​

Primary sedimentation tanks (PSTs) are the first stage of treatment following preliminary screening. They remove settleable solids and floating material through gravity settling, typically achieving 30-60% SS removal and 30-40% BOD removal.

UK PS208 Standards ​

Design Criteria ​

ParameterPS208 LimitUnitsNotes
Upflow velocity (DWF)≤ 1.2m/hAll tanks in service
Upflow velocity (FFT)≤ 2.0m/hAll tanks in service
Hydraulic retention time≥ 2.0hoursAt DWF minimum
Sidewater depth (SWD)≥ 2.5mMinimum operating depth
Weir loading (DWF)≤ 150m³/m/dEffluent weir overflow rate
Minimum tanks2-For N-1 compliance

N-1 Compliance ​

With one tank out of service for maintenance:

  • Upflow velocity at DWF ≤ 1.2 m/h
  • Upflow velocity at FFT ≤ 2.0 m/h
  • HRT at FFT ≥ 2 hours

Design Equations ​

Geometry Calculations ​

Radial (Circular) Tanks ​

Surface area:

A = π × (D/2)² = π × r²

Where:

  • A = surface area (m²)
  • D = diameter (m)
  • r = radius (m)

Volume:

V_cylindrical = A × SWD
V_conical = (1/3) × π × r² × h_cone
V_total = V_cylindrical + V_conical

where: h_cone = r × tan(θ)

Where:

  • SWD = sidewater depth (m)
  • θ = floor slope angle (degrees)
  • h_cone = height of conical section (m)

Typical dimensions:

  • Diameter: 15-40 m
  • SWD: 2.5-4.0 m
  • Floor slope: 8-12° (typical 10°)

Rectangular Tanks ​

Surface area:

A = L × W

Volume:

V = L × W × SWD

Where:

  • L = length (m)
  • W = width (m)

Typical dimensions:

  • Length: 20-60 m
  • Width: 5-15 m
  • Length:width ratio: 3:1 to 6:1

Hydraulic Calculations ​

Upflow Velocity (Surface Overflow Rate) ​

Formula:

V_up = Q / A / 24

Where:

  • V_up = upflow velocity (m/h)
  • Q = flow rate (m³/d)
  • A = total surface area (m²)
  • 24 = hours per day conversion

PS208 limits:

  • At DWF: ≤ 1.2 m/h
  • At FFT: ≤ 2.0 m/h

Physical meaning: Upflow velocity must be less than particle settling velocity for effective removal. Typical settling velocities:

  • Coarse solids: 3-5 m/h
  • Fine solids: 0.5-1.5 m/h
  • Design margin ensures capture of finer particles

Hydraulic Retention Time ​

Formula:

HRT = (V / Q) × 24

Where:

  • HRT = hydraulic retention time (hours)
  • V = tank volume (m³)
  • Q = flow rate (m³/d)

PS208 minimum: 2 hours at DWF

Typical values:

  • At DWF: 2-4 hours
  • At FFT: 1-2 hours

Removal Efficiency ​

Without Chemical Dosing ​

ParameterRemoval (%)Influent → Effluent
BOD30300 → 210 mg/L
SS50350 → 175 mg/L
NH₄-N037.5 → 37.5 mg/L
TP1512.5 → 10.6 mg/L

With Chemical Dosing (Fe or Al) ​

ParameterRemoval (%)Influent → Effluent
BOD40300 → 180 mg/L
SS60350 → 140 mg/L
NH₄-N037.5 → 37.5 mg/L
TP7012.5 → 3.75 mg/L

Effluent concentration:

C_eff = C_inf × (1 - E/100)

Where:

  • C_eff = effluent concentration (mg/L)
  • C_inf = influent concentration (mg/L)
  • E = removal efficiency (%)

Effluent load:

Load_eff = (C_eff × Q) / 1000

Where:

  • Load_eff = effluent load (kg/d)
  • Q = flow (m³/d)

Sludge Production ​

Primary Sludge Without Chemicals ​

Formula:

Sludge_dry = TSS_removed = TSS_inf × (E_SS / 100)
Sludge_flow = (Sludge_dry / 1000) / (DS% / 100)

Where:

  • TSS_removed = solids removed (kg/d)
  • TSS_inf = influent TSS load (kg/d)
  • E_SS = SS removal efficiency (%)
  • DS% = dry solids concentration (%, typical 3-5%)

Typical primary sludge characteristics:

  • Dry solids: 3-5% DS
  • Volatile solids: 65-75% of DS
  • Specific gravity: 1.02-1.05

With Chemical Dosing ​

Chemical sludge production adds to primary sludge (see Chemical Dosing):

Total_sludge = Primary_sludge + Chemical_sludge
Chemical_sludge = Fe_dose × 2.3 (kgSS/d)

Worked Example ​

Design Basis ​

  • Population: 5,000 PE
  • DWF: 600 m³/d
  • FFT (Formula A): 1,800 m³/d
  • Influent: BOD 300 mg/L, SS 350 mg/L

Step 1: Determine Number and Size of Tanks ​

Try 2 radial tanks, D = 25 m each:

Single tank area:

A = π × (25/2)² = π × 12.5² = 490.9 m²
Total area = 490.9 × 2 = 981.7 m²

Step 2: Check Upflow Velocity ​

At DWF (all tanks):

V_up = 600 / 981.7 / 24 = 0.025 m/h ✓
(Well below 1.2 m/h limit)

At FFT (all tanks):

V_up = 1800 / 981.7 / 24 = 0.076 m/h ✓
(Well below 2.0 m/h limit)

N-1 check (one tank out, area = 490.9 m²):

At DWF: V_up = 600 / 490.9 / 24 = 0.051 m/h ✓
At FFT: V_up = 1800 / 490.9 / 24 = 0.153 m/h ✓

Step 3: Determine Tank Depth ​

Choose SWD = 3.0 m, floor slope = 10°

Volume per tank:

V_cylindrical = 490.9 × 3.0 = 1,472.7 m³

h_cone = 12.5 × tan(10°) = 2.20 m
V_conical = (1/3) × π × 12.5² × 2.20 = 359.4 m³

V_total = 1,472.7 + 359.4 = 1,832.1 m³ per tank

Total volume = 1,832.1 × 2 = 3,664.2 m³

Step 4: Check HRT ​

At DWF:

HRT = (3664.2 / 600) × 24 = 146.6 hours ✓
(Well above 2 hour minimum)

At FFT:

HRT = (3664.2 / 1800) × 24 = 48.9 hours ✓

N-1 at FFT:

HRT = (1832.1 / 1800) × 24 = 24.4 hours ✓

Step 5: Calculate Sludge Production ​

Influent loads:

SS_load = (350 mg/L × 600 m³/d) / 1000 = 210 kgSS/d

Primary sludge (50% SS removal, 3% DS):

SS_removed = 210 × 0.50 = 105 kgSS/d
Sludge_flow = (105 / 1000) / 0.03 = 3.5 m³/d

Design Summary ​

ParameterValueCompliance
Configuration2 × radial tanks✓ N-1 capable
Diameter25 m each
SWD3.0 m✓ > 2.5 m
Total area981.7 m²
Total volume3,664 m³
Upflow (DWF)0.025 m/h✓ < 1.2 m/h
Upflow (FFT)0.076 m/h✓ < 2.0 m/h
HRT (DWF)146.6 hours✓ > 2 hours
Sludge production3.5 m³/d at 3% DS

UK Water Company Variations ​

UK Industry Practice ​

  • Upflow velocity: 1.0 m/h preferred (DWF)
  • HRT: 3 hours minimum preferred
  • Chemical dosing common for P removal

UK Industry Practice ​

  • Upflow velocity: 1.0-1.2 m/h (DWF)
  • Rectangular tanks preferred for large works
  • Storm tanks integrated with primary treatment

UK Industry Practice ​

  • SWD: 3.0 m typical minimum
  • N-1 compliance strictly enforced
  • Combined primary/storm tank arrangements

Design Considerations ​

Tank Configuration ​

Radial tanks advantages:

  • Efficient use of space (circular footprint)
  • Good for smaller-medium works (PE < 20,000)
  • Simple sludge collection with rotating scraper
  • Conical floor aids sludge thickening

Rectangular tanks advantages:

  • Better for large works (PE > 20,000)
  • Can accommodate multiple lanes
  • Easier to construct in linear site layouts
  • Simpler to cover for odor control

Inlet Arrangements ​

Radial tanks:

  • Central feed well with energy dissipation
  • Diameter = 15-20% of tank diameter
  • Inlet velocity < 0.3 m/s

Rectangular tanks:

  • End-feed with baffle wall
  • Cross-flow velocity < 0.15 m/s
  • Flow distribution across width

Outlet Arrangements ​

Weir loading:

W_load = Q / L_weir

Where:

  • W_load = weir loading (m³/m/d)
  • L_weir = total weir length (m)
  • PS208 limit: ≤ 150 m³/m/d

Radial tanks:

  • Peripheral weir (circumference = πD)
  • V-notch weirs for flow distribution

Rectangular tanks:

  • End weir across full width
  • Adjustable weirs for level control

Sludge Collection ​

Radial tanks:

  • Rotating scraper bridge (0.02-0.05 rpm)
  • Sludge withdrawn continuously or intermittently
  • Scraper torque monitoring for density control

Rectangular tanks:

  • Traveling bridge or chain-and-flight scrapers
  • Hopper spacing: 3-5 m
  • Sludge pumping cycles: 15-30 min intervals

Common Design Issues ​

Insufficient N-1 Capacity ​

Problem: Works designed with 2 tanks barely meeting criteria with both in service.

Solution: Size for N-1 from the outset. With 2 tanks, each must handle full DWF within limits.

High Weir Loading ​

Problem: Excessive weir overflow causing solids carryover.

Solution:

  • Increase weir length (use radial peripheral weir)
  • Add V-notch weirs for better distribution
  • Consider adjustable weirs

Poor Sludge Density ​

Problem: Thin sludge (< 2% DS) causing excessive volumes.

Solution:

  • Increase scraper frequency
  • Add sludge blanket monitoring
  • Consider pre-thickening
  • Check for septicity (add Fe for odor control)

Septicity and Odor ​

Problem: Anaerobic conditions in sludge causing H₂S.

Solution:

  • Reduce HRT if excessive (< 4 hours preferred)
  • Add ferric chloride (dual benefit: P removal + H₂S control)
  • Frequent sludge withdrawal
  • Consider covered tanks with odor treatment


References ​

  • UK Sewers for Adoption (7th Edition): Appendix PS208 - Primary Sedimentation Tanks
  • UK operator Design Standards: Primary treatment design criteria
  • CIWEM/WaPUG: Urban wastewater treatment design guidance

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