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Process Technology

Ammonia Stripping Systems

Remove high ammonia from industrial effluents and convert it into valuable fertilizer-grade ammonium sulphate without biological nitrification.

What is Ammonia Stripping?

Ammonia stripping is a physical-chemical process that removes dissolved ammonia (NH3/NH4+) from wastewater by shifting the equilibrium to gaseous NH3 through pH elevation and temperature, then stripping the gas with steam or air. The ammonia-rich gas is absorbed in sulphuric acid to produce ammonium sulphate, a marketable fertilizer. This process is ideal for high-strength ammonia streams (100-2,000 mg/L) where biological nitrification would be too slow, too expensive, or inhibited by other contaminants.

No Biological Process

Purely physical-chemical – no activated sludge, no nitrification bacteria, no sensitivity to toxins or temperature.

Byproduct Recovery

Ammonium sulphate fertilizer (21-0-0 NPK) sold to agriculture, offsetting 15-30% of operating overheads.

Rapid Removal

Single-pass reduction from 500 mg/L to <5 mg/L in minutes, compared to days for biological nitrification.

Steam Integration

Can use waste steam from boilers, evaporators, or WAO processes – zero additional energy requirement.

Process Steps

Step-by-step breakdown of the treatment process from influent to effluent.

01

pH Elevation to 10.5-11.0

Caustic soda (NaOH) or lime raises pH to shift ammonium equilibrium from NH4+ to volatile NH3 gas. Online pH control maintains setpoint within ±0.2.

02

Preheating to 60-80°C

Wastewater preheated by heat exchanger using stripped effluent or waste steam. Higher temperature increases NH3 partial pressure for faster stripping.

03

Counter-Current Stripping Column

Packed tower (Raschig rings or structured packing) with counter-current steam or air flow. NH3 transfers from liquid to gas phase. 95-99% removal achieved.

04

Acid Absorption

Ammonia-rich gas enters absorption tower with sulphuric acid mist. Reaction: 2NH3 + H2SO4 → (NH4)2SO4. Product solution at 40% concentration crystallised to solid fertilizer.

05

Effluent pH Readjustment

Stripped effluent pH 10.5 readjusted to 7.0-8.0 with CO2 or sulphuric acid for discharge or downstream treatment. Residual ammonia <5 mg/L.

Typical Performance

99%
Ammonia removal
<5
mg/L residual NH3
500-2000
mg/L inlet range
21-0-0
NPK fertilizer grade

Equipment Used in This Process

Explore the equipment components that make this process effective.

Where This Process is Applied

WAO Effluent

Stripping ammonia from wet air oxidation effluent before RO polishing.

Coke Oven Wastewater

Ammonia 800-1,500 mg/L from coke production stripped to <15 mg/L.

Chemical Manufacturing

High-ammonia process streams where advanced biological treatment is inhibited.

Agricultural Fertilizer

Ammonium sulphate byproduct sold to local farms as nitrogen fertilizer.

Related Processes & Technologies

Process Fundamentals & Design

This treatment stage is engineered to achieve specific contaminant removal targets while providing stable, predictable performance across variable inlet conditions. Design parameters are calculated from wastewater characterisation data, regulatory requirements, and site-specific constraints including footprint, energy availability, and operator capability.

Process Optimisation

Design validated by CFD modelling and pilot testing to confirm performance guarantees.

Mechanical Reliability

Equipment selected for 20-year design life with minimal wearing parts and easy access.

Chemical Efficiency

Automated dosing and feedback control minimise reagent consumption and sludge production.

Compliance Assurance

Online monitoring and data logging demonstrate continuous consent compliance.

Design Parameters

Design Flow10 – 5,000 m³/h (application specific)
Inlet VariabilityDesigned for 1:3 peak-to-average flow ratio
Removal Efficiency85 – 99% depending on target contaminant
Hydraulic RetentionCalculated from kinetic constants and safety factors
Power Consumption0.5 – 5.0 kWh/100 m³ (process dependent)
Chemical DoseAuto-controlled based on online analysers
Sludge Production0.2 – 1.5 kg DS/kg contaminant removed
MaterialsSS304, SS316L, or carbon steel with coating

Integration with Treatment Train

No treatment stage operates in isolation. This process is designed to receive conditioned influent from upstream stages and deliver effluent quality suitable for downstream processes. Hydraulic and organic loading rates are balanced across the complete treatment train to prevent bottlenecking and ensure overall plant efficiency. Our engineers model the complete flowsheet to optimise Capital expenditure and Operating expenditure across the plant lifecycle.

Upstream Protection

Screening, equalisation, and pre-treatment protect this stage from damage and overload.

Downstream Conditioning

Effluent quality ensures downstream biology, filtration, or disinfection performs optimally.

Recycle Streams

Reject streams, filtrate, and centrate are routed back to appropriate upstream points.

Packed Tower Design & Mass Transfer Calculations

From Henry's Law to HTU/NTU — the engineering behind column sizing.

Ammonia equilibrium & Henry's Law

The fraction of total ammonia present as volatile NH3 (vs ionic NH4+) is governed by pH and temperature:

NH3 fraction = 1 / (1 + 10(pKa − pH))

where pKa = 0.09018 + 2729.92/T (T in Kelvin). At 25°C, pKa ≈ 9.25. At pH 11, >98% is NH3; at pH 7, <1% is NH3.

Henry's Law constant for NH3 increases strongly with temperature:

T (°C)H (atm·m³/mol)% NH3 at pH 10.5
201.7 × 10−594%
403.8 × 10−594%
607.5 × 10−594%
801.3 × 10−495%

HTU/NTU design method

Column height Z = HTU × NTU, where:

HTU = G / (KGa × P × A)

NTU = ∫ (dY / (Y − Y*))

G = molar gas flow (kmol/h), KGa = overall mass transfer coefficient (kmol/m³/h/atm), P = total pressure (atm), A = column cross-section (m²), Y = gas-phase NH3 mole fraction, Y* = equilibrium mole fraction.

Typical design values for steam stripping of high-strength ammonia:

  • HTU: 0.3–0.8 m (structured packing); 0.6–1.5 m (random Raschig rings)
  • NTU: 3–6 for 95% removal; 5–8 for 99% removal
  • Steam ratio: 1.2–2.5 kg steam / kg NH3 removed
  • Superficial gas velocity: 0.5–1.5 m/s
  • Liquid loading: 10–40 m³/m²/h

Corrosion Resistance & Construction Materials

ComponentConditionsRecommended MaterialAlternative
Stripping column shellpH 10.5–11, 60–80°C, NH3SS316L clad carbon steelSS2205 duplex
Structured packingHigh pH, erosionSS316LPTFE-coated SS
Absorption towerH2SO4 mist, 40–60°CSS316L / PTFE linedHastelloy C-276
Heat exchanger (influent)pH 10.5, scaling riskSS316L plateTitanium (if chlorides >1,000 mg/L)
Piping (NaOH)50% NaOH, ambientCarbon steelSS304 (for <40%)
Piping (H2SO4)93–98%, ambientCarbon steel (passivated)SS316L for dilute acid
PumpsCaustic / hot ammoniaSS316L or Alloy 20Mag-drive for sealing

Common Operational Issues & Solutions

Poor removal efficiency

Check pH is >10.5 at column inlet. Verify steam flow and temperature (>100°C superheated preferred). Inspect packing for fouling (CaCO3 scaling from hard water) or channeling. Packing pressure drop should be 5–15 mbar/m; higher indicates blockage.

Foaming in column

Surfactants in coke-oven or chemical wastewater cause stable foam, raising pressure drop and carry-over. Install foam breaker spray nozzles at column top; consider antifoam dosing (polypropylene glycol, 5–20 ppm). Monitor differential pressure as early indicator.

Low ammonium sulphate concentration

Product concentration depends on H2SO4 flow and NH3 gas rate. If <35% w/w, increase acid stoichiometry to 1.05–1.10 mol H2SO4 / mol NH3. Check for acid dilution from condensate carry-over.

Heat exchanger fouling

High-pH preheated wastewater precipitates calcium carbonate and magnesium hydroxide on heat exchanger plates. Maintain inlet pH <10.8 if hardness >300 mg/L CaCO3, or install softening pre-treatment. Schedule acid cleaning (5% citric) every 3–6 months.

Operating Cost Breakdown & Byproduct Value

Cost per kg NH3-N removed

Cost ItemTypical (/kg N)Notes
Caustic soda (NaOH)0.15–0.25pH 10.5–11.0; 3.5–4.5 kg/kg N
Sulphuric acid0.08–0.122.9 kg H2SO4 / kg N
Steam0.10–0.40If waste steam: near zero
Power (pumps, blowers)0.03–0.055–15 kWh/100 m³
Labor & maintenance0.05–0.10Proportional to plant size
Total Operating expenditure0.40–0.90Before byproduct credit
Byproduct credit (NH4)2SO4−0.10–−0.2521-0-0 fertiliser, –350/t
Net Operating expenditure0.25–0.70Highly variable by site

Comparison with biological nitrification

FactorStrippingBiological Nitrification
Capital expenditure (500 m³/d)–1.5M–2.0M
Operating expenditure (/kg N)0.25–0.700.40–0.80
Start-up timeHours2–6 weeks
Inhibitor sensitivityNoneHigh (heavy metals, phenols)
Sludge productionMinimal0.15–0.25 kg TSS/kg N
ByproductFertiliserNone (N&sub2; gas)
FootprintCompactLarge (aeration + clarifier)
Best inlet NH3200–2,000 mg/L<100 mg/L preferred

Need This Process for Your Application?

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Industries We Serve

Our expertise spans multiple industries with sector-specific water treatment solutions.