Technical Scheme for Development of Gas Turbine SCR Treatment System — Design of Urea Injection System and Control System (Chapter 1)

Technical Scheme for Development of Gas Turbine SCR Treatment System — Design of Urea Injection System and Control System (Chapter 1)

              

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
  1. 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.

  1. 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

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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

 

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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