Daniel Lieder (TU Braunschweig) built a chemical reactor network (CRN) for the RQL combustor of the P200-SX. My measurements calibrate and test it. Against the Jet A-1 data of the ASME paper, it reproduces outlet temperature, EI CO₂ and EI CO within 4.5%. It overpredicts NOₓ by about 1.8×. In the GPPS fuel comparison, it predicts the measured fuel-induced changes in \(T_{t4}\), CO₂ and NOₓ within 1 percentage point. It does not predict the particle-number change.
Aircraft emission estimates usually come from semi-empirical correlations, such as the Boeing Fuel Flow Method 2 (BFFM2), fitted to certification data. They are quick, but they are calibrated for conventional jet fuel. They also capture operating-point effects only through correlation [1]. A chemical reactor network (CRN) models the physics instead. Each combustor zone becomes an idealized reactor with finite-rate chemistry, so fuel composition and operating point enter directly.
The micro-turbojet makes this testable. Its RQL (rich-burn, quick-quench, lean-burn) reverse-flow combustor follows the same combustion pathway as many full-scale engines. At maximum thrust, its combustor-inlet temperature and pressure are close to those of a turbofan at idle [4]. The match holds at that selected point only. The measured engine state and emissions calibrate the model at some operating points and test it at others.
![Structure of the CRN combustor model. Air at splits between the primary (PZ), secondary (SZ) and dilution (DZ) zones. The PZ is a bank of perfectly stirred reactors. The SZ and DZ are plug-flow reactors with unmixed fractions. From Lieder, Sharma et al. [[1]].](fig/crn-asme-structure.png)
The primary zone is a bank of 21 perfectly stirred reactors. Their equivalence ratios follow a normal distribution, which represents unmixedness. The secondary and dilution zones are plug-flow reactors that keep a fraction of the flow unmixed. At each operating point, the engine performance model supplies \(p_{t3}\), \(T_{t3}\), the air flow and the fuel–air ratio [1, 3]. The air flow is calculated.
Mean primary-zone equivalence ratio, and the width of its distribution from an unmixedness correlation. The 21 reactors cover \(0\) to \(2\phi_{PZ}\) [3].
Air split between zones, and reactor residence time. The calibration parameters are the zone volumes, the air splits and the unmixed fractions.
The chemistry is a finite-rate mechanism with 621 species and 27,829 reactions. It includes a sectional soot model from 2 to 202 nm. It uses surrogate formulations for Jet A-1 (H/C 1.96) and FT-SPK (H/C 2.17) [3]. The calibration searches the parameter space and minimizes the summed error over operating points and targets:
In the ASME study, three operating points (25, 50 and 100% thrust) calibrate the model. Two more (30 and 70%) are held back as validation points [1].
![Combustor-outlet temperature against relative thrust: CRN model vs measurement, with the calibration points boxed [[1]].](fig/crn-asme-tt4.png)
Each result below comes from one campaign. The campaigns differ in date, operating points and model calibration, so their deviations do not combine into one accuracy figure.
ASME study, Jet A-1, five operating points. The model reproduces the measured \(T_{t4}\), EI CO₂ and EI CO with a maximum deviation of 4.5% [1].
The deviations at the two validation points (30 and 70% thrust) stay in the range of the calibration points [1]. The paper takes this as validation of the operating-point trend.
The model overpredicts NOₓ by about 1.8×. The paper links this to the temperature inhomogeneity in the small combustor, which the network does not resolve [1]. The CICS study adds that the model does not include radiative heat loss [2].
CICS study, Jet A-1, three thrust levels. In this campaign, the model overpredicts \(T_{t4}\) by 3–5.5% and CO₂ by 3–3.5%. CO deviates by up to 23% at the highest thrust, and NOₓ is 66–130% high [2].
![Emission indices of CO₂, CO and NOₓ against relative thrust: CRN model (circles) vs measurement (stars), with the calibration points boxed [[1]].](fig/crn-asme-ei.png)
GPPS study, Jet A-1 vs FT-SPK at maximum thrust. The model keeps the same parameters for both fuels, and only the surrogate changes. It predicts the fuel-induced change to within 1 percentage point for \(T_{t4}\), EI CO₂ and EI NOₓ [3]:
| Quantity | Measured change | CRN change | CRN absolute error (Jet A-1 / FT-SPK) |
|---|---|---|---|
| \(T_{t4}\) | −1.5% | −1.8% | +3.4% / +3.0% |
| EI CO₂ | −1.7% | −1.3% | +3.4% / +3.8% |
| EI NOₓ | −4% | −4% | about +70% / +70% |
| EI CO | +0.5% | +3.7% | +10% / +14% |
The model therefore gets the direction and size of the change right for \(T_{t4}\), CO₂ and NOₓ, while the absolute NOₓ stays about 70% high. For CO, it overpredicts the small measured increase.
![Gaseous emission indices of CO₂, CO and NOₓ for Jet A-1 and FT-SPK at maximum thrust: CRN model (solid) vs experiment (hatched). The percentages give the change from Jet A-1 to FT-SPK. Reproduced from Lieder, Sharma et al. [[3]] under CC BY-NC-ND 4.0.](fig/crn-gpps-ei-fuels.png)
![Loss-corrected soot number size distributions at 50, 70 and 100% thrust: experiment (markers) vs CRN (dashed). The loss correction grows steeply below about 5 nm, so the smallest bins are the least certain [[2,3]].](fig/crn-cics-soot-psd.png)
In the CICS Jet A-1 data, the CRN reproduces how the soot size distribution moves with operating point. But it puts the maximum at too small a diameter and overpredicts the small sizes [2]. The loss-corrected distribution maximum is at 3.8, 3.9 and 4.3 nm at 50, 70 and 100% thrust.
In the GPPS fuel comparison, the measured soot mass fell by 72% with FT-SPK, and the model predicts 67%. The measured mass uses a unit effective density for both fuels [3].
Particle number disagrees. The measured number rose by 38%, while the model predicts a 77% decrease. The measured rise comes only from the smallest bins, where the loss correction is largest. Across almost all other sizes, the measured FT-SPK distribution is lower [3].
The model also overpredicts the absolute soot mass by a factor of 20–26 and the number by a factor of 8–11 [3]. Particle formation is the weakest part of the network.
The ASME study recalibrates the CRN for an IAE V2500-A1 with ICAO certification data at the four LTO points. No separate validation points exist for that engine [1]. The recalibrated model matches the ICAO data within 18.2% for CO and 8.3% for NOₓ.
The study then compares two methods that predict emissions along a full flight trajectory: the CRN coupled to an engine performance model, and BFFM2. The two differ by up to 30% in CO at static sea level, and by up to 60% in flight [1]. No full-scale measurement exists along the trajectory, so this compares the methods with each other.
The paper attributes the larger in-flight difference to the CRN modeling altitude and Mach-number effects that BFFM2 only corrects for [1]. The micro-turbojet and V2500 models also show similar zone-by-zone progressions. That supports transferring the model structure to the larger engine.