| Item | Content |
|---|---|
| Project Name | Gas Turbine SCR Denitration Aftertreatment System |
| Document No. | SCR-GT-001 |
| Version | V1.0 |
| Preparation Date | July 25, 2026 |
| Prepared by | Bi Yajie, Technical Department |
This document is the technical development scheme for the gas turbine SCR denitration aftertreatment system, and it shall guide the subsequent detailed design, equipment procurement and control system development.
| Item | Description |
|---|---|
| Security Classification | Internal |
| Distribution Scope | Project Team, Customer, Design Institute |
| Relevant Standards | HJ 562-2010 Technical Specification for Flue Gas Denitration Engineering of Thermal Power Plants — Selective Catalytic Reduction Method, GB/T 21508, HJ 2001-2010 |
| Preceding Documents | Gas Turbine Exhaust Parameters, Reactor Outline Drawing, Emission Requirements |
- Overview The customer requires SCR denitration aftertreatment for gas turbine flue gas to meet the following emission targets: reduce NOₓ from 25 ppm to 2 ppm (denitration efficiency of 92%), reduce CO from 25 ppm to 2 ppm, and limit NH₃ slip ≤ 3 ppm.
Ammonia injection was adopted in the original proposal. However, considering safety, storage and transportation cost, system complexity and operation & maintenance convenience comprehensively, this project recommends switching to 32.5% urea aqueous solution (AdBlue) for SCR reducing agent supply.
The gas turbine parameters provided by the customer are relatively limited at present, including only exhaust parameters and partial reactor outline dimensions. Key data such as catalyst layer position, NOₓ conversion reference basis and inlet O₂ content are missing. Therefore, this scheme carries out feasibility analysis and conceptual design first, and detailed calculation and verification will be performed after the supplementary data are available.
- Feasibility Analysis 2.1 Summary of Original Design Parameters 2.1.1 Reactor Geometry (Decomposed according to drawings provided by the manufacturer)
| Parameter | Value | Remarks |
|---|---|---|
| Inlet Diameter | Dn 2007.73 mm (≈ DN2000) | Circular Nozzle |
| Outlet Diameter | Dn 2704.49 mm (≈ DN2700) | Large Rectangular Cross-section |
| Total Axial Length | 11 800 mm | Reducer Transition Flue Duct |
| Inlet Straight Pipe Section | 2 190 mm | DN2000 Cylindrical Nozzle |
| Expansion Transition Section | 6 360 mm + 1 851 mm | Trapezoidal Wedge-shaped Reducer |
| Outlet Straight Pipe Section | 3 282 mm + 5 100 mm + 4 151.96 mm | DN2700 |
| Inlet Flange Section | 938.4 mm | Connected to Gas Turbine Exhaust |
| Outlet Flange Section | 634.91 mm | Connected to Downstream Flue Duct |
Structural Judgment: This equipment is a reducer transition flue duct, not the main body of the SCR reactor. One end is a DN2000 cylindrical nozzle connected to the gas turbine exhaust, and the other end is a large rectangular cross-section connected to the main body of the SCR reactor or the waste heat boiler. The focus of the modification work is on the DN2000 inlet side.
2.1.2 Flue Gas Operating Conditions
| Operating Case | Ambient Temperature (℃) | Flue Gas Flow (10⁴ Nm³/h) | Flue Gas Flow (t/h) | Flue Gas Temperature (℃) |
|---|---|---|---|---|
| 1 | -10 | 31.6 | 401.5 | 510 |
| 2 | 0 | 31.5 | 400.2 | 512 |
| 3 | 15 | 31.1 | 394.0 | 515 |
| 4 | 30 | 30.0 | 380.3 | 523 |
| 5 | 40 | 29.0 | 368.0 | 529 |
Note: All 5 operating cases are under full-load operation. Case 1 is selected as the design point (worst-case condition: maximum flue gas flow and minimum ambient temperature).
2.1.3 Emission Requirements
| Item | Inlet Concentration | Outlet Concentration | Removal Efficiency |
|---|---|---|---|
| NOₓ | 25 ppm | 2 ppm | 92% |
| CO | 25 ppm | 2 ppm | 92% |
| NH₃ Slip | — | ≤ 3 ppm | — |
Note: The conversion reference basis for NOₓ and CO (dry basis at 15% O₂ or others) shall be confirmed by the manufacturer. This scheme is calculated directly based on the given ppm values for the time being.
2.2 Feasibility Analysis 2.2.1 Temperature Condition Is Fully Satisfied
| Parameter | Value / Range | Judgment |
|---|---|---|
| Urea Thermal Decomposition Temperature | Starts at 350 ℃, complete thermal decomposition at 400 ℃ | Much lower than flue gas temperature |
| Optimal Reaction Temperature for NH₃-SCR | 350–450 ℃ | Satisfied |
| Catalyst Sintering Temperature | > 650 ℃ | Large safety margin |
| Actual Flue Gas Temperature | 510–529 ℃ | Optimal temperature window |
Conclusion: The flue gas temperature of 510–529 ℃ falls within the optimal temperature window for the SCR + urea solution, fully satisfying the requirements for thermal decomposition, reaction and catalyst safety.
2.2.2 Inlet Flow Velocity Calculation (based on Case 1, the worst-case condition) Inlet cross-sectional area: \(A_\text{in} = \pi/4 \times 2.0077^2 \approx 3.165\ \text{m}^2\) Standard volumetric flow rate: \(Q_\text{N} = 31.6 \times 10^4 / 3600 \approx 87.78\ \text{Nm}^3/\text{s}\) Operating volumetric flow rate (510 ℃, \(\rho \approx 0.485\ \text{kg/m}^3\)): \(Q \approx 87.78 \times (273 + 510)/273 \approx 251.9\ \text{m}^3/\text{s}\) Actual flue gas velocity: \(v = Q / A_\text{in} \approx 251.9 / 3.165 \approx 11.8\ \text{m/s}\)
Conclusion: The inlet flow velocity is approximately 12 m/s, which is within the typical velocity range of SCR flue ducts (8–15 m/s). The flow field is reasonable and the pressure drop is controllable.
2.2.3 Cold Zone Effect Calculation (based on Case 1)
| Effect | Calculated Value | Remarks |
|---|---|---|
| Urea Solution Flow Rate | Approx. 72 kg/h | 32.5% AdBlue, estimated at NH₃/NOₓ equivalence ratio of 0.95 |
| Water Content | 67.5% × 72 ≈ 48.6 kg/h | Water evaporation |
| Heat Absorption for Water Evaporation | 48.6 × 2257 ≈ 109.7 MJ/h ≈ 30.5 kW | Major heat sink |
| Heat Absorption for Urea Thermal Decomposition | Approx. 3–5 kW | CO(NH₂)₂ → NH₃ + HNCO |
| Total Enthalpy of Flue Gas (Case 1) | Approx. 20.8 MW | Based on cp=1.05 kJ/kg·K |
| Theoretical Overall Temperature Drop | Approx. 1.5–2.0 ℃ | Negligible |
| Local Cold Zone Temperature Drop | < 15 ℃ | Atomization core region |
Conclusion: The overall temperature drop is less than 2 ℃, which is far below the allowable temperature fluctuation of the catalyst. The local cold zone temperature drop is controlled within 15 ℃ and can be further reduced by optimizing the atomization and layout of the injectors.
2.2.4 Pressure Drop Assessment
| Item | Pressure Drop (Pa) | Remarks |
|---|---|---|
| Injectors and AIG Mixing Elements | 200–400 | Air-assisted nozzles + support structure |
| Catalyst Bed | 800–1500 | Depends on catalyst type and bed thickness |
| Static Mixer (if applicable) | 150–300 | Optional |
| Expanding / Contracting Duct | 50–150 | Existing geometry |
| Total | 1200–2350 (approx. 1.2–2.4 kPa) | Typically allowable 3–5 kPa for gas turbine SCR |
Conclusion: The total system pressure drop is approximately 1.2–2.4 kPa, which falls within the typical allowable range of 3–5 kPa for gas turbine SCR aftertreatment. The pressure drop design is reasonable.
2.3 Overall Conclusion Based on the analysis of temperature, flow velocity, cold zone effect and pressure drop, the urea-injection SCR scheme adopted for this project is fully engineering-feasible. The technical challenge lies in the injector arrangement, atomization and mixing under large cross-section and high flow rate conditions. Reasonable AIG array design and CFD verification are required to guarantee the uniformity of NH₃/NOₓ mixing.
3.Technical Scheme 3.1 Nozzle Type Selection
3.1 Nozzle Type Selection
| Type | Atomized Particle Size SMD | Uniformity | Compressed Air Requirement | Recommendation Index |
|---|---|---|---|---|
| Air-Assist Nozzle | 20–40 μm | Good | 4–6 bar compressed air | ★★★★★ |
| Pressure Atomizing Nozzle | 50–80 μm | Fair | No compressed air required | ★★ |
| Ultrasonic Atomization | 10–20 μm | Good | Ultrasonic power supply required | ★★★ |
| Steam/Air Two-Fluid | 15–30 μm | Good | Steam source required | ★★★ |
Recommended: Adopt air-assist nozzles for atomization with 4–6 bar compressed air, controlling the SMD at approximately 30 μm. This solution features fine atomization, stable operation and convenient maintenance, making it the first choice for large-cross-section SCR systems.
3.2 Key Design Parameters of the Spray Nozzle
| Parameter | Design Value | Design Basis |
|---|---|---|
| Nozzle Orifice Diameter | 0.5–1.2 mm | Larger orifice for higher flow rate |
| Spray Angle | 30°–45° solid cone | Solid cone provides more uniform coverage |
| Spray Direction | Concurrent with flue gas flow | Avoid disturbance from counter flow |
| Atomizing Air Pressure | 4–6 bar | Determines SMD |
| Atomizing Gas-Liquid Mass Ratio | 0.5–1.5 | Affects atomization fineness |
| Lance Insertion Depth | 250–350 mm | Excessive depth leads to burnout/erosion; insufficient depth results in poor coverage |
| Number of Lances | 6 pcs | AIG array (1 central + 5 outer ring) |
| Lance Material | 316L stainless steel | Resistant to urea corrosion |
| Lance Cooling Method | Natural air cooling or outer protective sleeve | For high-temperature environment |
3.3 Lance Layout Scheme 3.3.1 Layout Principles For the large cross-section of DN2000, a single lance cannot cover the entire flow channel, so an AIG (Ammonia Injection Grid) array must be adopted. The recommended layout is as follows:
| Item | Design Value |
|---|---|
| Number of Lances | 6 pcs (1 central + 5 outer ring) |
| Position of Outer-ring Lances | At radius of 500 mm (approx. 0.5R) |
| Angular Spacing of Outer Ring | Evenly spaced at 60° |
| Lance Insertion Position | At the end of the inlet straight pipe section, 200–300 mm from the start of the expansion section |
| Spray Direction | 30° included angle with flue gas flow (co-current inclined insertion) |
| Insertion Depth | 250–350 mm |
| Installation Method | Flange sealing + bellows compensation (for thermal expansion prevention) |
3.3.2 Side View of AIG Lance Array
Figure 1 Side View of AIG Lance Array (Z-X Plane, 30° Co-current Inclined Insertion)
3.3.3 Cross-section View of AIG Lance Array
Figure 2 Cross-section View of AIG Lance Array (DN2000 Pipe, Plum Blossom Layout with 1 Central + 5 Outer-ring Lances)
3.3.4 CFD Simulation of Lance Mixing
CFD simulation is adopted to verify the lance atomization, urea pyrolysis and NH₃/NOₓ mixing process, so as to ensure the uniformity of NH₃/NOₓ molar ratio distribution at the catalyst inlet cross-section (CV ≤ 5%). Key simulation focuses:
| Simulation Content | Key Concerns |
|---|---|
| Evolution of Atomized Particle Size | SMD decreases from 150 μm to below 30 μm, and evaporation is completed within 500 mm |
| Urea Pyrolysis Process | CO(NH2)2→NH3+HNCO, completed within 800 mm |
| Temperature Distribution | Temperature drop in local cold zones < 15 ℃ |
| NH₃ Uniformity | CV ≤ 5% at the catalyst inlet |
| Pressure Drop Verification | Compare with the estimated value in Section 2.2.4 |
3.4 Estimation of Atomizing Compressed Air Consumption
| Item | Value | Remarks |
|---|---|---|
| Urea Solution Flow Rate (Case 1) | Approx. 72 kg/h | 32.5% AdBlue |
| Volume Flow Rate of Urea Solution | Approx. 68 L/h | Density ≈ 1.06 kg/L |
| Atomizing Gas-Liquid Mass Ratio | 1.0 | Recommended value |
| Total Atomizing Air Flow Rate | Approx. 72 kg/h ≈ 2.0 Nm³/min | Standard condition |
| Air Flow per Lance | Approx. 12 kg/h | Evenly distributed among 6 lances |
| Recommended Air Compressor Capacity | ≥ 2.5 Nm³/min, 6 bar | Including 20% margin |
Compressed air quality requirement: The air must be oil-free and water-free. It is recommended to use an adsorption dryer to reduce the dew point below -40 °C to prevent nozzle blockage by crystal deposition.
3.5 Injection Flow Control Scheme
| Control Method | Accuracy | Cost | Recommendation Index |
|---|---|---|---|
| Main pipe metering + 6 branch manual balancing valves | ±10% | Low | Alternative |
| 6 sets of independent metering pumps + flow closed-loop control | ±2% | Medium | Recommended |
It is recommended to adopt 6 sets of independent metering systems (one set for each lance), which facilitates single-lance calibration, fault isolation and on-line maintenance.
4. Design Target Estimation (Based on the most unfavorable Case 1)
| Parameter | Value | Remarks |
|---|---|---|
| Inlet NOₓ Concentration | 25 ppm | Conversion basis to be confirmed by the supplier |
| NOₓ Removal Efficiency | 92% | 25 → 2 ppm |
| Outlet NOₓ | 2 ppm | Design target |
| NH₃ Injection Rate | Approx. 35 kg/h | Converted to pure NH₃ |
| Urea Solution (32.5%) Flow Rate | Approx. 72 kg/h | Approx. 68 L/h |
| Injection Rate per Lance | Approx. 12 kg/h | Approx. 11.3 L/h |
| Atomizing Air Flow Rate | Approx. 72 kg/h | Approx. 2.0 Nm³/min |
| Overall Temperature Drop | < 2 ℃ | Negligible |
| Temperature Drop in Local Cold Zones | < 15 ℃ | Atomization core region |
| Required Mixing Distance | Approx. 5 m | To be achieved within the 6.3 m expansion section |
Note: The above values are conceptual design estimates. The final design shall be verified by the seven-in-one SCR calculation tool with complete supplementary data provided by the supplier.
5.3 Data to be Supplied by the Supplier
The data currently provided by the supplier is insufficient for detailed design. The following information shall be supplemented in accordance with the Data Sheet Provided by the Gas Turbine SCR Control System Supplier:
| No. | Data to be Supplied | Impact |
|---|---|---|
| 1 | NOₓ conversion basis (dry base, 15% O₂ or others) | Governs urea dosage calculation |
| 2 | Position and thickness of catalyst layers inside the SCR reactor | Determines pressure drop and efficiency |
| 3 | Feasibility of opening holes on DN2000 inlet straight pipe section (wall thickness, reinforcement) | Determines AIG installation method |
| 4 | Material and thermal insulation condition of the existing flue duct | Determines welding and heat tracing scheme |
| 5 | Gas turbine power signal interface and communication protocol | Determines control system scheme |
| 6 | Source and parameters of compressed air (pressure, flow rate, dew point) | Determines air compressor and drying equipment selection |
Post time: Oct-28-2026