How to Select an SCR Catalyst
Part of the SCR DeNOx: The Complete Guide — this article is one of the detailed pages in the guide.
Direct answer: SCR catalyst selection runs through six decisions in order: (1) characterize the gas — temperature, NOx, SO₂, dust, moisture; (2) fix the temperature window and required NOx removal; (3) choose geometry (plate vs honeycomb) from dust and erosion; (4) size the catalyst volume with a deactivation margin; (5) run a poison audit from the fuel and upstream process; (6) verify by simulation testing on the actual gas. Skipping any step converts a catalyst choice into a field problem.
Step 1: Characterize the gas
| Parameter | Why it matters |
|---|---|
| NOx inlet and NO/NO₂ split | Sets required removal and NH₃ demand |
| Gas temperature at catalyst | Selects the catalyst formulation window |
| SO₂ / SO₃ | Drives bisulfate risk and SO₂→SO₃ oxidation limit |
| Dust concentration & particle size | Decides geometry and pitch |
| Moisture | Affects acid dew point downstream |
| O₂ | SCR needs oxygen present |
Typical conventional SCR operating window is 200–420 °C; below ~200 °C choose a low-temperature formulation, and understand the bisulfate trade-off (see Low-Temperature SCR).
Step 2: Set the removal target
Design NOx removal of 80–95% is typical for permit-driven duties. Higher removal needs more volume, tighter NH₃ control and cleaner gas. The NH₃/NOx molar ratio operating range is about 0.8–1.05 — beyond 1.0 ammonia slip rises steeply.
Step 3: Choose geometry
- Plate — wider pitch, better for high-dust and sticky ash; see Plate vs Honeycomb.
- Honeycomb — higher surface per volume, lower volume for the same activity; fine for low-dust gas.
Face velocity, channel pitch and erosion margin follow from the dust analysis (see Ash & Erosion).
Step 4: Size the volume
Volume follows from space velocity and required conversion, then a deactivation margin is applied for the expected life (see Volume Calculation). Typical space velocity range is 2,000–8,000 h⁻¹ depending on gas and target — a design value, not a product guarantee.
Step 5: Run the poison audit
The fuel and upstream process decide catalyst life:
- Alkali/alkaline-earth metals (biomass, waste) — see Catalyst Poisoning
- SO₂ and ammonium bisulfate — see Ammonia Slip Control
- Arsenic, phosphorus — fossil and some industrial fuels
- Silica fines — erosion
The same NOx target can need 20–40% more volume on a high-poisoning fuel.
Step 6: Verify before commitment
Simulation testing on the actual flue gas (see SCR Activity Testing) confirms conversion, SO₂ oxidation and pressure drop at the design conditions. This is standard practice before large orders.
When SCR is not the right choice
- Flue gas temperature far below the window with no reheating budget — evaluate SNCR or staging.
- Very high SO₃ with no upstream control — catalyst poisoning dominates economics.
- Variable fuel with unknown poison profile — resolve fuel security first.
- Space or pressure-drop constraints that no catalyst geometry satisfies.
Related pages
- SCR vs SNCR — technology-level choice
- Reactor Positioning — where the catalyst sits in the duct
- Reducing Agent Systems — NH₃/urea supply