Membrane Bioreactor (MBR) Wastewater Design Simulator Back
Wastewater / MBR

Membrane Bioreactor (MBR) Wastewater Design Simulator

Size a membrane bioreactor (MBR) and watch the reactor volume, required membrane area, permeability, fouling rate and CIP interval respond in real time. Tune influent flow, BOD, MLSS, SRT, design flux and TMP to land a design that runs stably without crippling the membranes.

Parameters
Module configuration
Submerged = hollow fibre (Toray/Mitsubishi); flat-sheet = Kubota K-3; external = tubular
Influent flow Q
m³/day
Influent BOD
mg/L
150–300 for municipal sewage, 500–1500 for food-industry waste
MLSS
mg/L
Mixed-liquor suspended solids. 8,000–15,000 is the MBR working range
SRT (sludge age)
day
At least 15 days is required for full nitrification
Design flux J
LMH
L/m²/h. 15–25 is the stable range; above 30 forces frequent CIP
TMP (trans-membrane pressure)
kPa
Clean-start 10–30, just-before-CIP 40–60
Results
BOD load (kg/day)
Reactor volume (m³)
HRT (hr)
Membrane area (m²)
Permeability (LMH/kPa)
CIP interval (day)
MBR tank cross-section — hollow-fibre module and air scour

Hollow-fibre modules are immersed in the activated-sludge tank (MLSS). Coarse air bubbles from the diffuser scour the membrane surface while permeate is sucked from inside the fibres.

TMP over time (fouling curve)
Energy by configuration (kWh/m³)
Theory & Key Formulas

$$V = \frac{Y_{obs}\,S_0\,Q\,SRT}{X_v},\qquad A_{membrane} = \frac{Q}{J},\qquad L_p = \frac{J}{\Delta P}$$

Reactor volume V, required membrane area A and permeability L_p. Y_obs: observed yield, S_0: influent BOD, X_v: MLVSS (≈0.8·MLSS), J: design flux, ΔP: trans-membrane pressure TMP.

$$Y_{obs} = \frac{Y}{1+k_d\,SRT},\qquad P_{x,vss} = Y_{obs}\,S_0\,Q$$

Apparent yield corrected for SRT and waste-sludge production. We assume Y=0.4 (sludge yield) and k_d=0.05 day⁻¹ (endogenous decay). Longer SRT lowers Y_obs and shrinks the waste-sludge stream.

$$\text{foulingRate} \propto J^{2},\qquad T_{CIP} = \frac{30\ \text{kPa}}{\text{foulingRate}}$$

Pushing the flux up makes fouling progress super-linearly, shortening the time to a +30 kPa TMP rise and therefore the CIP interval. Operating costs change sharply around 15 LMH.

Membrane Bioreactor (MBR) — Flux and Fouling Design

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An MBR is basically activated sludge with a membrane instead of a clarifier, right? I have heard that there is no final settling tank.
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Exactly. Conventional activated sludge (CAS) puts a clarifier downstream and lets the sludge settle by gravity. An MBR replaces that step with a UF or MF membrane, pore size around 0.04–0.4 μm, that does the solid–liquid separation physically. So the permeate is essentially SS-free and virtually free of E. coli too. Singapore’s NEWater, Paris Seine Aval and the Beijing Olympic reuse plant are all classic large-scale references.
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The water quality argument I get, but membranes are expensive. Is being allowed to run at a higher MLSS really worth it?
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That is the core of the MBR. CAS is capped at about 1,500–3,000 mg/L MLSS because anything denser will not settle. An MBR can be pushed to 8,000–15,000 mg/L since the membrane never fails to separate, so the reactor volume needed for the same BOD load shrinks roughly five-fold. Try the MLSS slider on the left and you will see V drop almost inversely. On top of that, a 20–30 day SRT lets the slow-growing nitrifiers accumulate, so you also nitrify ammonia completely.
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If I raise the design flux, the membrane area Q/J drops, which sounds great. Is there an upper limit?
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That is the trap. Yes, A=Q/J halves when you double the flux, but the fouling rate goes roughly as J². Try pushing J from 25 to 35 LMH here: the CIP interval collapses from 42 days into the low teens. A cleaning that should be monthly becomes weekly, and both chemical cost and membrane lifetime suffer. That is why we stay below the so-called critical flux — about 25–30 LMH for municipal sewage.
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How do you fight the fouling itself? Is it only about washing the membranes?
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Three layers. First, air scouring: coarse bubbles from below rise along the hollow fibres and physically shear the cake layer. That is by far the biggest energy item in an MBR — typically 60–70% of total kWh/m³ goes into scour air. Second, backwash: filter for nine minutes, then push permeate backwards for one minute to recover internal pore blocking. Third, CIP: monthly soak with about 500 mg/L NaOCl for organic fouling, plus citric acid every six months or so for inorganic scale. Flat-sheet modules also accept mechanical vibration, which slightly lowers scour energy.
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So pushing flux to save on membranes raises operating cost instead. Where is the total minimum?
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For municipal submerged MBRs the life-cycle cost bottoms out around year-average 18–22 LMH, given membrane prices of 30–50 USD/m², CIP chemicals at a few USD/m²·year and 0.4–0.6 kWh/m³ of scour energy. In this tool, J=20, MLSS≈12,000 and SRT≈25 gives an ok verdict with the CIP interval around a month. That is essentially the modern MBR design point. After that, all you add is a 1.2–1.5 safety factor on membrane area to cover diurnal and seasonal peaks, and the real-world design is basically done.

Frequently Asked Questions

For submerged municipal MBRs, the standard year-average design flux is 15–25 LMH (L/m²/h). Above 30 LMH the TMP rises steeply and chemical cleaning (CIP) becomes much more frequent. This tool computes the required membrane area as A=Q/J and estimates the CIP interval assuming foulingRate ∝ J². A lower flux means more membrane area, but the total energy plus chemicals cost typically reaches a minimum around 18–22 LMH.
Because the membrane provides a complete solids–liquid separation, MBRs can run at MLSS 8,000–15,000 mg/L, about five times the level used in conventional activated sludge (CAS). SRT is normally 20–30 days to support complete nitrification. A longer SRT reduces the observed yield Y_obs = Y/(1+kd·SRT) and shrinks the waste-sludge stream, but it also raises MLSS, increasing fouling risk and aeration energy. Sweep MLSS and SRT in this tool to balance reactor volume and HRT.
When the trans-membrane pressure (TMP) rises by about +30 kPa from the clean-start value, a chemical-in-place (CIP) cleaning with sodium hypochlorite (NaOCl) or citric acid is required. This tool estimates foulingRate = max(0.1, (J/15)²·0.5) kPa/day and shows CIP interval = 30 / foulingRate. At the default J=18 LMH the interval is about 42 days, i.e. roughly monthly CIP. Pushing flux above 25 LMH shrinks the interval to 2–3 weeks and operating cost rises sharply.
Submerged hollow-fibre modules (Toray, Mitsubishi, ZeeWeed, etc.) have the best energy efficiency and dominate large municipal and industrial MBRs. Flat-sheet panels (Kubota K-3) are mechanically robust and easy to clean, so they suit food-and-beverage wastewaters. External tubular MBRs use a fast cross-flow and are picked for very high-viscosity or high-SS streams such as digestate. Switching the configuration in this tool changes the aeration-energy bar so you can see that external MBRs are dominated by recirculation-pump power.

Real-world Applications

Large-scale municipal sewage: Reference projects such as Paris Seine Aval (a 300,000 m³/day MBR stage), the Beijing Olympic reuse plant and the Singapore Changi NEWater factory show MBRs at city scale. They replace CAS + sand filtration + UV disinfection in a single step, shrinking the footprint to a third or half of a conventional plant. Inputting Q=50,000–100,000 m³/day in this tool quickly shows that 100,000 m² of membrane area is a realistic order of magnitude.

Food and beverage wastewater: Streams from Coca-Cola, Pepsi or breweries carry BOD of 500–2,000 mg/L plus suspended solids, fats and oils. An MBR delivers a complete solid–liquid split that lets the site reuse the permeate for cooling-towers or wash-down, hitting discharge limits and water cost at the same time. Flat-sheet Kubota K-3 modules are popular here for their easy cleaning.

Decentralised and small-scale treatment: Hotels, resorts, remote islands and container ships lack a sewer connection. MBRs are compact, start up quickly and automate easily. At Q=50–500 m³/day they are now often more efficient than a CAS plus MF train. Try the bottom end of the flow slider in this tool.

Water reuse: MBR permeate is essentially SS-free and bacteria-free, which makes it an ideal pre-treatment for downstream reverse osmosis (RO). A reuse train such as "activated sludge → MBR → RO → UV" is the de-facto standard for NEWater-style industrial and indirect potable reuse. If the MBR is not running stably, the downstream RO fouls aggressively, so the CIP management this tool helps you size really determines the stability of the whole reuse chain.

Common Misconceptions and Pitfalls

The biggest trap is the simple-minded view that "higher flux means less membrane and lower capex". Yes, A=Q/J halves when you double the flux, but the fouling rate goes roughly as J², so doubling the flux quadruples fouling. The CIP interval drops by a factor of four (monthly cleaning becomes twice a week), annual chemical cost roughly multiplies by five and membrane life shrinks. Add in extra scour air to keep the membrane surface shear up, and energy explodes too. On a Life-Cycle-Cost basis the optimum almost always sits at 18–22 LMH. Don't let a vendor talk you into an aggressively high design flux without checking the resulting CIP interval and membrane area together in a tool like this.

Second, the idea that "if MLSS goes up the reactor can shrink without limit". Volume does scale roughly as 1/MLSS in theory, but above 15,000 mg/L the sludge viscosity jumps, the oxygen-transfer α-factor drops below 0.5 and aeration power has to more than double. The fouling layer on the membrane also gets thicker, accelerating TMP rise. Real MBRs typically settle around 10,000–13,000 mg/L MLSS, where compaction and aeration efficiency balance out. Anything beyond that is research territory. If you key in MLSS=18,000 here the computed volume is small, but please remember that the real plant behaves very differently.

Finally, the over-confidence that "as long as the permeate looks clean, MBR solves everything". An MBR removes SS and bacteria perfectly, but soluble COD, nutrients (N and P) and trace pollutants (pharmaceuticals, PFAS) need their own removal mechanisms. Nitrogen removal requires nitrification + denitrification stages, phosphorus removal needs either chemical precipitation or biological-P configurations such as A2O. PFAS and recalcitrant organics need activated carbon or RO behind the MBR. The MBR is the gold standard for physical separation, not a substitute for biological or chemical treatment.

How to Use

  1. Enter influent flow rate (m³/day), typically 100–500 m³/day for municipal treatment plants
  2. Input influent BOD concentration (mg/L), commonly 200–400 mg/L for domestic wastewater
  3. Set mixed liquor suspended solids (MLSS) target, usually 8,000–12,000 mg/L for MBR systems
  4. Specify sludge retention time (SRT) in days; 15–30 days balances nitrification and membrane fouling
  5. Review calculated reactor volume, membrane area (m²), and permeability (LMH/kPa) to verify feasibility
  6. Adjust parameters iteratively until HRT exceeds 6 hours and CIP interval reaches 7+ days

Worked Example

Municipal plant treating 250 m³/day influent with 300 mg/L BOD, 10,000 mg/L MLSS, and 20-day SRT: BOD load = 75 kg/day; reactor volume = 125 m³; HRT = 12 hours; membrane area = 62.5 m² (assuming 4 LMH flux); permeability = 0.08 LMH/kPa (hollow-fibre membranes); CIP interval = 14 days. Increasing SRT to 25 days raises reactor volume to 156 m³, reducing organic loading and extending membrane life.

Practical Notes

  1. MLSS above 12,000 mg/L increases viscosity and membrane fouling; cap at 12,000 mg/L for submerged modules
  2. HRT below 4 hours risks inadequate nitrification; extend SRT to 25–30 days for nitrogen removal
  3. Permeability degradation occurs monthly; schedule CIP (clean-in-place) before fouling resistance exceeds 0.5 bar
  4. Membrane flux of 20–30 LMH typical for aerobic MBRs; higher flux requires tighter membrane specifications (0.04 µm)