Appearance
Aerobic Zone
Aerated biological reactor zone for carbonaceous oxidation, nitrification, and biological phosphorus uptake.
Overview
The aerobic zone is the primary treatment zone in activated sludge systems. Under aerobic conditions (DO > 1.5 mg/L), heterotrophs oxidize organic matter while autotrophs convert ammonia to nitrate.
Functions
- BOD/COD oxidation
- Nitrification (ammonia → nitrate)
- Phosphorus uptake (in BNR systems)
- Endogenous respiration
Biochemistry
Carbon Oxidation
$$C_{org} + O_2 → CO_2 + H_2O + \Delta biomass$$
Rate: $$r_s = \mu_{max} \times \frac{S}{K_s + S} \times \frac{DO}{K_O + DO} \times X$$
Nitrification
Step 1 - Nitritification (AOB): $$NH_4^+ + 1.5O_2 → NO_2^- + 2H^+ + H_2O$$
Step 2 - Nitratification (NOB): $$NO_2^- + 0.5O_2 → NO_3^-$$
Overall: $$NH_4^+ + 2O_2 → NO_3^- + 2H^+ + H_2O$$
Oxygen requirement: 4.57 mg O₂/mg NH₄-N
ASM1 Kinetics
Autotrophic growth: $$\mu_A = \mu_{A,max} \times \frac{S_{NH}}{K_{NH} + S_{NH}} \times \frac{S_O}{K_{O,A} + S_O}$$
Temperature correction: $$\mu_{A,max}(T) = \mu_{A,max}(20) \times 1.07^{(T-20)}$$
Phosphorus Uptake (ASM2d)
In aerobic conditions, PAOs take up excess phosphorus:
$$P_{uptake} = Y_P \times VFA_{stored}$$
Requires prior anaerobic VFA storage.
Design Equations
Minimum SRT for Nitrification
$$SRT_{min} = \frac{1}{\mu_{A,max} - b_A}$$
At 12°C: SRT_min ≈ 4-5 days Design SRT = 2-3 × SRT_min
Oxygen Demand
Carbonaceous: $$OD_C = \frac{Q \times (S_0 - S)}{f} \times (1 - 1.42 \times Y_{obs})$$
Nitrogenous: $$OD_N = 4.57 \times Q \times (TKN_0 - TKN_e - 0.12 \times P_x)$$
Total: $$OD_{total} = OD_C + OD_N - OD_{denit}$$
Where denitrification credit: 2.86 mg O₂/mg NO₃-N removed
Aeration Requirement
$$AOR = \frac{OD_{total}}{SOTE \times \alpha \times \beta \times \theta^{(T-20)}}$$
Parameters
Operating Parameters
| Parameter | Unit | Default | Range | Description |
|---|---|---|---|---|
| DO setpoint | mg/L | 2.0 | 1.5-4.0 | Target DO |
| MLSS | mg/L | 3500 | 2000-6000 | Mixed liquor |
| SRT | days | 12 | 5-25 | Solids retention |
| HRT | hours | 4 | 2-8 | Hydraulic retention |
| Temperature | °C | 15 | 10-25 | Operating temp |
Design Parameters
| Parameter | Unit | Default | Range | Description |
|---|---|---|---|---|
| Volume | m³ | calculated | - | Zone volume |
| Volume fraction | % | 60 | 50-75 | Of total biological |
| KLa | h⁻¹ | 10 | 5-30 | Transfer coefficient |
| α factor | - | 0.6 | 0.4-0.9 | Alpha correction |
| SOTE | % | 25 | 15-35 | Fine bubble |
Kinetic Parameters
| Parameter | Symbol | Unit | Default | Range |
|---|---|---|---|---|
| Max autotrophic growth | μ_A,max | d⁻¹ | 0.8 | 0.3-1.5 |
| Autotrophic decay | b_A | d⁻¹ | 0.15 | 0.05-0.25 |
| NH₄ half-saturation | K_NH | mg/L | 1.0 | 0.5-2.0 |
| O₂ half-saturation (AOB) | K_O,A | mg/L | 0.5 | 0.2-1.0 |
Aeration Systems
Fine Bubble Diffusers
- SOTE: 20-35%
- Air flow: 2-5 Nm³/m²/h
- Floor coverage: 10-15%
- Most energy efficient
Coarse Bubble
- SOTE: 8-12%
- Used for mixing
- Lower efficiency
Mechanical Aerators
- Surface aerators
- Brush rotors (oxidation ditch)
- 1.5-2.5 kg O₂/kWh
Control Strategies
| Strategy | Description | Energy Saving |
|---|---|---|
| DO feedback | Maintain setpoint | Baseline |
| Ammonia-based | DO proportional to NH₄ | 10-20% |
| ABAC | Ammonia-based aeration control | 20-30% |
| MPC | Model predictive | 25-35% |
Configuration
Example Configuration
json
{
"type": "aerobicZone",
"id": "main-aeration",
"parameters": {
"volume": 4000,
"doSetpoint": 2.0,
"mlss": 3500,
"srt": 12,
"aeration": {
"type": "fineBubble",
"diffuserType": "membrane",
"floorCoverage": 0.12,
"sote": 0.25,
"kla": 10,
"alpha": 0.6,
"beta": 0.95
},
"control": {
"strategy": "ammoniaFeedback",
"doMin": 1.0,
"doMax": 4.0,
"ammoniaSP": 1.0
}
}
}DO Profiles
Uniform DO
- Constant setpoint throughout
- Simple control
- May over-aerate
Tapered Aeration
- Higher DO at inlet
- Matches oxygen demand
- Energy efficient
Intermittent Aeration
- Alternating aeration/mixing
- Simultaneous nitrification/denitrification
- For SND applications
Troubleshooting
| Issue | Cause | Solution |
|---|---|---|
| High effluent NH₄ | Low SRT | Increase SRT |
| Low DO | Increase aeration | |
| Low temperature | Extend volume | |
| High effluent NO₃ | No denitrification | Add anoxic zone |
| Foaming | Nocardia/Microthrix | Reduce SRT, add selector |
| Rising sludge | High NO₃ to clarifier | Increase denitrification |
Related Topics
References
- Metcalf & Eddy (2014). Wastewater Engineering, 5th Ed.
- WEF (2018). Design of Municipal Wastewater Treatment Plants, MOP 8.
- Rosso, D. et al. (2008). "Aeration of Large-Scale WWTPs".