JET-CALF (Jet Contrails from Aviation Lubricants and Fuels) is a multi-institution program on how fuels and lubricants affect aircraft emissions and contrails. I lead the micro-turbojet performance and gaseous-emissions task, and I coordinate the UBC experimental work for JET-CALF, SCALE-SAF and VLAME. Back-to-back tests on a JetCat P200-SX compare fuel use, gaseous emissions and particles for Jet A-1 and FT-SPK. Each result below belongs to one campaign on this one engine.
Sustainable aviation fuels are drop-in fuels, but they do not all burn the same way. Their composition changes evaporation, mixing, reaction rates and heat release. Measurements on a full-scale turbofan are slow, regulated and expensive. As a result, fuel effects are usually seen only at a few certification points [1]. The Research page explains why a micro-turbojet is a useful platform for this work.
The rig is useful at one selected comparison point. At maximum thrust, the P200-SX reaches a combustor-inlet temperature and pressure close to those of a V2500 turbofan at idle. We call this the “micro-max, macro-idle” comparison [1, 2].
The match is in the combustor-inlet state only. Residence time, mixing, pressure-ratio range and the lubricant input still differ. The small engine is therefore not a scale model of the turbofan [1].
![Combustor-inlet temperature and pressure against relative thrust for the P200-SX (left) and a V2500 turbofan (right, data from Göing [[2]]). The P200-SX maximum and the V2500 idle point are within 16 K and 24 kPa of each other.](fig/micro-vs-turbofan-tt3-pt3.png)
| Operating point | \(T_{t3}\) | \(p_{t3}\) | OPR | Fuel flow |
|---|---|---|---|---|
| P200-SX at max thrust | 469 K | 374.8 kPa | ≈ 4 | 0.0103 kg/s |
| V2500 at idle | 453 K | 351 kPa | ≈ 3.5 | 0.0988 kg/s |

Boeing and NSERC fund JET-CALF. The program connects UBC, TU Braunschweig (IFAS), Tampere University and Sungkyunkwan University. The partners share the work as follows:
I lead the micro-turbojet task. I plan and run the campaigns, make the performance and gaseous-emissions measurements, and do the data reduction and uncertainty analysis. I also supply the measured engine state that calibrates the CRN model [3].
Jan Göing of TU Braunschweig joined us at UBC on a research stay. Together we made the alternative-fuel measurements on our engine at UBC. The IFAS institute reported the work in its news, in German: Analyse des Einflusses alternativer Kraftstoffe auf Performance und Emissionen ↗.


We test the fuels one after the other, on the same day and engine, at the same operating points. This keeps engine-to-engine and day-to-day effects small, so the remaining difference is mainly the fuel. Full-scale campaigns struggle to make that comparison.
![P200-SX cutaway with the gas and fuel paths and the measurement stations. Total pressure and temperature are measured at the compressor exit (3), turbine inlet (4) and nozzle exit (8). From Lieder et al., ASME JEGTP [[3]].](fig/asme-engine-stations.png)
The performance channels are thrust (load cell), spool speed, fuel flow, and \(p_t, T_t\) at stations 3, 4 and 8. Two lines sample the exhaust [1, 4]:


Emission indices come from a carbon balance on the diluted line. All species share the same denominator, the fuel carbon seen as CO₂ above background plus CO. In the numerator, only CO₂ has its background subtracted [4, 5]:
Molar mass \(M_i\), fuel carbon mass fraction \(Y_C\), combustion efficiency \(\eta_{\mathrm{comb}}\) (from the earlier CRN study), and diluted-line (DL) and background (bg) dry mole fractions. Background CO₂ was 450 ppm and background CO was 0 ppm in the GPPS campaign [5].
I propagate the uncertainty to first order from the analyzer accuracies and combine it in quadrature, following SAE ARP1533D [6].
| Analyzer | Species | Accuracy |
|---|---|---|
| 2B Tech Model 405 nm | NOₓ | ±2% |
| Teledyne API T300U | CO | ±1% |
| LI-COR LI-850 | CO₂ | ±1.5% |
The analyzers do not see some of the carbon: unburned hydrocarbons and lubricant volatiles from the engine’s open-loop oil system. An indirect check through the catalytic stripper puts this carbon below 6% of the total at the lowest operating point. It is lower at higher load. The check cannot separate fuel-derived from lubricant-derived carbon. Non-volatile particles carry less than 1% of the fuel carbon [1].

FT-SPK is less dense than Jet A-1, but it carries more energy per kilogram. In the March 2026 campaign, it needed 8.5%, 6.5% and 5.0% more fuel by volume at 80, 90 and 100% corrected speed. By mass, it needed about 2% more at 80% and about 1.5% less at 100%. The two fuels cross near 90%.
The fuel meter measures volume. The mass-based values therefore depend on the fuel densities used for the conversion.

I measure the density and specific gravity of the Jet A and FT-SPK fuels with a portable density meter (Fig. 9). These values convert the metered volume into fuel mass.
The separate GPPS back-to-back test at maximum thrust shows the same direction, with different sizes. Volumetric TSFC rose by 4.3% and gravimetric TSFC fell by 5.3%. The measured combustor-outlet temperature \(T_{t4}\) dropped by 1.5% [5].
The two campaigns use different speed corrections and density inputs. I keep their numbers separate.
| Jet A-1 | FT-SPK | Change | |
|---|---|---|---|
| Thrust \(F_N\) | 205 N | 208 N | +1.5% |
| \(p_{t3}\) / \(T_{t3}\) | 369 kPa / 468 K | 370 kPa / 468 K | matched |
| Volume fuel flow (measured) | 1.21 × 10⁻⁵ m³/s | 1.28 × 10⁻⁵ m³/s | +6% |
| Fuel mass flow (from density) | 0.0101 kg/s | 0.0097 kg/s | −4% |
| \(T_{t4}\) (measured) | 1240 K | 1222 K | −1.5% |
| TSFC by volume / by mass | +4.3% / −5.3% |
The Result view in the gallery above shows the emission indices of the March 2026 campaign at 80, 90 and 100% speed. CO falls and NOₓ rises with power, the same directions as the V2500 certification data [1].
In that campaign, FT-SPK has lower EI CO₂ at all three speeds. EI NOₓ is lower at 90 and 100%, and the same within uncertainty at 80%. The CO difference between the fuels is inside the error bars at every speed.
The GPPS test at maximum thrust gives EI CO₂ −1.7%, EI NOₓ −4% and EI CO +0.5% with FT-SPK [5]. Neither campaign shows a clear CO reduction.
The particle mass result is clearer than the number result. Soot mass fell by 72%, computed from sizes with a unit effective density [5]. Particle number rose by 38%, but that increase comes only from the smallest bins, where the loss correction is largest. Across almost the whole size range, the FT-SPK distribution was lower [5].
The CRN model predicts the FT-SPK change in \(T_{t4}\), EI CO₂ and EI NOₓ to within 1 percentage point of the measured change. For example, measured \(T_{t4}\) fell by 1.5% and the model gives 1.8%. The absolute values are still off: the model is about 3% high in \(T_{t4}\) and 70% high in NOₓ [5].