Outside of Working Hours +90 552 876 55 30 info@arsistek.com
Countries We Operate In 21 countries with on-site experience and engineering support
Our Global Market Experience · Browse country details for field references, regulation insights and engineering support
See All Countries
Request a Quote

Phosphorus Removal in MBR Treatment: Method, Efficiency, Cost

September 25, 2025 5 dk okuma 95 görüntülenme
Phosphorus removal in MBR systems is achieved through biological (EBPR) and chemical methods. With the right combination, effluent phosphorus can be reduced to below 0.3-0.5 mg/L. In this guide, you will find process selection, chemical dosage calculation, cost comparison, and 7 common mistakes encountered in the field.
Phosphorus Removal in MBR Treatment: Method, Efficiency, Cost

Phosphorus removal in MBR (Membrane Bioreactor) systems is one of the most critical steps in modern wastewater treatment. The 2 mg/L discharge limit set for total phosphorus (TP) in the Water Pollution Control Regulation can be reduced to 1 mg/L and even 0.5 mg/L levels for sensitive receiving environments. MBR technology is an advanced treatment solution that can easily meet these limits with proper design and operation.

In this guide, we share phosphorus removal methods in MBR systems, real field data, cost analysis, and practical knowledge gained from our 20+ years of industrial wastewater treatment experience.

What is Phosphorus Removal in MBR Systems?

Phosphorus removal in MBR systems is the process of removing both dissolved and particulate phosphorus from wastewater before it is discharged into the receiving environment, using both biological and chemical processes. The ultrafiltration (UF) membrane of the MBR provides a 30-50% higher particulate phosphorus removal efficiency compared to conventional systems.

Typical Performance Values

  • Influent total phosphorus (TP): 6-15 mg/L (domestic), 10-50 mg/L (industrial)
  • Effluent TP (biological only): 1-3 mg/L
  • Effluent TP (biological + chemical): 0.3-0.8 mg/L
  • Effluent AKM: < 1 mg/L (thanks to the UF membrane)
  • Efficiency: 92-98% total phosphorus removal

Phosphorus Removal Methods in MBR

1. Biological Phosphorus Removal (EBPR – Enhanced Biological Phosphorus Removal)

The EBPR method is based on the principle that phosphate-accumulating organisms (PAO – Phosphate Accumulating Organisms) accumulate phosphorus inside the cell in an environment that alternates between anaerobic and aerobic conditions.

Process flow:

  1. Anaerobic zone: PAOs consume VFA (Volatile Fatty Acids) and release intracellular polyphosphate
  2. Aerobic zone: The same PAOs then take up phosphorus excessively from the environment (luxury uptake)
  3. Sludge discharge: High phosphorus content sludge is removed from the system

Advantages:

  • No chemical usage (low operating cost)
  • Sludge can be valorized (potential for phosphorus recovery)
  • Sustainable (positive in ESG reporting)

Disadvantages:

  • Requires operator control (sensitive process)
  • Efficiency decreases in cold weather (T < 10 °C)
  • Cannot guarantee effluent TP < 1 mg/L alone

2. Chemical Phosphorus Removal (Precipitation)

The chemical method involves precipitating phosphorus with metal salts (aluminum or iron-based). The most commonly used chemicals in MBR systems are:

  • Ferric Chloride (FeCl₃): Most common, effective, economical
  • Aluminum Sulfate (Al₂(SO₄)₃ – Alum): Effective at low pH
  • PAC (Polyaluminum Chloride): Produces less sludge
  • Ferrous Sulfate (FeSO₄): Economical but requires oxidation

Chemical Dosage Calculation (Practical Formula)

Stoichiometrically, 1 mg P requires 1.8 mg Fe or 0.87 mg Al. Due to inefficiencies occurring in the field, the dosage is taken 1.5-2 times higher:

  • FeCl₃ dosage: 3-5 mg Fe / mg P (to be removed)
  • Alum (Al₂(SO₄)₃) dosage: 1.5-2.5 mg Al / mg P

Example calculation: In an MBR facility with a flow rate of 1000 m³/day, if the influent TP = 8 mg/L and the target effluent = 0.5 mg/L, the phosphorus to be removed = 7.5 mg/L = 7.5 kg/day. Accordingly, FeCl₃ requirement: 7.5 × 4 = 30 kg Fe/day (≈ 75 kg FeCl₃ 40% solution).

3. Hybrid Method (Most Common and Recommended)

The most successful results in industrial wastewater treatment are achieved with a biological + chemical hybrid approach:

  • Reduce effluent TP to 1-2 mg/L with EBPR
  • Use online chemical dosing to bring it down below 0.3-0.5 mg/L during peak moments
  • Chemical consumption occurs only when necessary → minimum operating cost

Advantage of MBR in Phosphorus Removal: UF Membrane

While the effluent in classical activated sludge systems is separated by sedimentation, an 0.04-0.4 micron pore size UF membrane is used in MBR. This provides a critical advantage in terms of phosphorus removal:

  • Particulate phosphorus is completely retained (5-10% escapes in classical systems)
  • Can operate with high MLSS (8-12 g/L) → increases biological activity
  • More compact bioreactor → flexible chemical dosing point
  • During backwashing, the accumulation on the membrane is removed, ensuring continuous high efficiency

Cost Comparison: Biological vs Chemical vs Hybrid

A 1-year comparison in an industrial MBR facility with a flow rate of 1000 m³/day (example):

  • Only biological (EBPR):
    • Investment: 15-20% more expensive (extra zone)
    • Operation: Very low (no chemicals)
    • Efficiency risk: Can drop 20-30% in cold weather
  • Only chemical:
    • Investment: Low (dosing pump + tank)
    • Operation: Annual high chemical cost (approximately 6-12 times that of biological) (depending on flow rate)
    • Sludge production: Increases by 20-30% (waste disposal cost)
  • Hybrid (Recommended):
    • Investment: Medium
    • Operation: Annual medium chemical cost (approximately 2-4 times that of biological, only during peak times) (only during peaks)
    • Efficiency: Guarantees 0.3-0.5 mg/L
    • 25-35% total cost savings over 3-5 years

7 Common Mistakes Encountered in the Field

  1. Incorrect selection of dosing point: FeCl₃ should be dosed at the end of the aerobic zone; it negatively affects PAOs in the anaerobic zone
  2. Excessive chemical usage: 30% excess dosage for a 5% efficiency increase → not economical
  3. Lack of online TP measurement: Real-time control is not possible with manual sampling; online TP measurement is essential for automatic dosing control
  4. Short sludge age in EBPR: If SRT (Sludge Retention Time) < 8 days, PAOs cannot reproduce sufficiently
  5. Membrane fouling accumulation: Iron hydroxide accumulates on the membrane; regular chemical cleaning (CIP) is essential
  6. Failure to control pH: Optimum pH is 6.0-7.5; if the upper limit is exceeded, metal hydroxide accumulates and does not precipitate
  7. High nitrate recirculation: Entry of NO₃⁻ into the anaerobic zone of EBPR → PAO inhibition, decreases phosphorus removal

Which Sectors is MBR + Phosphorus Removal Critical For?

  • Dairy and food industry: High phosphorus detergent and milk protein wastes
  • Beverage production facilities: High TP after anaerobic fermentation
  • Textile finishing facilities: Phosphorus in dye complexes
  • Hotels and resort complexes: Near sensitive receiving environments (sea, lake)
  • Municipal wastewater facilities: New EU directives are heading towards a 0.5 mg/L limit
  • Pharmaceutical and chemical facilities: Specific process wastes

Use in Conjunction with Water Recovery

After phosphorus is reduced to below 0.5 mg/L in MBR, the effluent can be sent to the RO (Reverse Osmosis) system, allowing for 85-95% water recovery. In this case, phosphorus is concentrated in the RO concentrate and becomes a recoverable by-product (for the fertilizer industry).

Conclusion: The Importance of Proper Design

Phosphorus removal in MBR systems is successful not only by adding chemical dosage but also through the integrated design of the entire process. The anaerobic zone volume, SRT, chemical dosing point, online monitoring, and sludge management are interconnected parameters.

As Arsistek Arıtma A.Ş., we have commissioned over 150 projects in the last 20 years. We offer site analysis, wastewater characterization, process design, manufacturing, installation, and long-term operational support in MBR + phosphorus removal. Contact us for consultancy and a free preliminary study for your specific project.

Projeniz İçin Teklif Alın

Atıksu arıtma çözümleriniz için ön bütçe, mühendislik tasarımı ve saha ziyareti — uzman ekibimizle ücretsiz değerlendirme.

Request a Quote
S
Yazar
Site Yöneticisi

Atıksu arıtma uzmanı, çevre mühendisi. Endüstriyel su arıtma projelerinde 20+ yıl saha deneyimi.

Share:

Frequently Asked Questions

7 Soru
With MBR, a phosphorus removal efficiency of 75-85% with biological (EBPR) method, 90-98% with chemical coagulation, and 95-99% with hybrid (biological + chemical polishing) method is achieved. UF membrane filtration retains phosphorus particles as well, resulting in lower P values from MBR output compared to conventional activated sludge.
The decision depends on 4 factors: discharge limit, wastewater C/N/P ratio, operating budget, sludge disposal cost. Limit 1-2 mg/L: biological EBPR is sufficient. Limit <0.5 mg/L: biological + chemical polishing is required. Limit <0.3 mg/L: chemical coagulation (FeCl₃ or aluminum) is mandatory.
EBPR is based on the operation of PAO bacteria (Polyphosphate Accumulating Organisms) that store phosphorus as polyphosphate (poly-P) within the cell in an anaerobic-aerobic cycle. In the anaerobic phase, phosphorus is released, and in the aerobic phase, 2-3 times more is recovered. Net effect: removal of phosphorus from the system with waste sludge.
There are 4 common options: FeCl₃ (ferric chloride) is the most common, inexpensive, and effective. Al₂(SO₄)₃ (alum) is an alternative. PAC (poly-aluminum chloride) is effective at a lower dosage. FeSO₄ is economical but less efficient. The dosage is typically adjusted to a Fe/P or Al/P mol ratio between 1.5-2.5.
Cost levels (relative): Biological EBPR is at the lowest level (only energy + anaerobic volume). Chemical dosing is approximately 5-10 times that of biology (FeCl₃ + excess sludge disposal). Hybrid approach is approximately 2-4 times that of biology. In tight limits, the hybrid solution is optimal in terms of safety and cost.
Yes, however, a multi-barrier approach is essential: (1) MBR with EBPR configuration + (2) chemical dosing (Fe/Al) + (3) UF membrane filtration retains particles P. With this trio, the total P output can be consistently maintained in the range of 0.1-0.3 mg/L. This configuration is standard for the AB sensitive receptor environment directive.
5 critical errors: (1) Insufficient HRT in the anaerobic zone (should be at least 1-2 hours), (2) Oxygen escape in the anaerobic zone (kills PAO bacteria), (3) Insufficient VFA (easy biological carbon source), (4) Very high pH (reduces chemical efficiency), (5) Excessively long sludge SRT (washes out PAO).

Bu Kategoriden Diğer Yazılar

What is Package Treatment? Definition, Components, and Areas of Use

Packaged treatment is a compact version of a wastewater treatment plant that is pre-manufa...

22.05.2026
How Are Industrial Wastewaters Treated? Comprehensive Engineering Guid...

Industrial wastewater exhibits radically different compositions and variability compared t...

22.05.2026
Package Treatment Capacities and Sizing Guide: Correct System Selectio...

The most critical decision in selecting a packaged treatment system is determining the cor...

22.05.2026
Write via WhatsApp Get a Quick Quote