1. Introduction
Air quality degradation has several aspects such as: gaseous pollution, global warming, O
3 layer depletion and the main reason is the burning of fossil fuels [
1]. Therefore, the use of renewable energy may be a solution for slowing if not stopping the processes involved in air quality degradation.
In terms of aviation fuels, several alternatives have been pointed out by the researchers: the use of alcohols, hydrogen (both liquid and gaseous), synthetic fuels, etc. [
2] Nowadays, in the field of aviation fuels the main research is focused on the production and use of bio-fuels which are prove to be more environmentally friendly, have the potential to reduce the greenhouse gasses and CO
2 emissions. [
3]
The most promising bio-fuel in aviation applications seems to be the biodiesel because it shows the highest potential to meet the needed energy requirements [
4,
5]. It appears to be the most feasible solution to O
3 depletion and environment degradation by successfully replacing classical fuels. It is well established that biodiesel emit fewer gaseous pollutants during burning and its most important advantage is that it can be used in diesel engines without retrofitting them. It also shows lower toxicity, biodegradation and being a renewable fuel can successfully replace classic diesel. [
6,
7]
On the other hand, alcohols seem to be an equally good solution, especially during use in piston engines. [
8,
9,
10] Ethanol is one of the most important alcohols used in piston engines and studies have been conducted on its use. By covering aspects from ethanol production to engine performances while using gasoline/bioethanol blends (E3, E6 and E10) to gaseous emissions [
11], researches have pushed the boundary towards on-board hydrogen production and mixtures made out of alcohol and diesel [
12], alcohol and di-methyl carbonate [
13]. Also, classes of alcohols (methanol, ethanol, butanol, etc.) have been tested in different mixtures with gasoline and their effect on engine’s performances and emissions have been assessed. [
14]
It has been studied the improvements brought in terms of engine performances when alcohols have been mixed with gasoline. Thus, the adding of small amounts of alcohol not influence the engine’s delivered properties (thrust, fuel consumption, etc.) [
15]. CO
2 and total emitted hydrocarbons (THC) increase with the increase of alcohol percentage within the blend [
16]. Thus, de adding of the alcohol contribute to the improvement of thermal efficiency and anti-detonation properties of the fuel [
17], therefore, larger concentrations ranging from 10 to 85% and even 100% of ethanol in gasoline have been tested. [
18,
19,
20]
In terms of the use of alcohols in different mixtures for feeding aviation turbo-engines, there have been conducted several studies depending on the type of engine and its required performances. Few of them have been finalized also with demonstrative flights. [
21,
22,
23]
Besides engines’ performances assessing, researches have been focused also on the evaluation of the combustion and gaseous pollutant emissions. [
24,
25,
26,
27,
28,
29].
Mixtures of ethanol and Jet-A aviation fuel have been used to fed different types of engines starting from GTM-140 micro-turbine, full-size DGEN380 turbofan to four-stroke direct injection diesel engine. [
30,
31].
Nevertheless, first tests and certifications on the use of biodiesel/airplane fuel (AVGAS) blends have been made for aviation piston engines [
32] but also ethanol/Jet-A mixtures have been tested on piston aviation engines [
33]. It has been determined that by using a new type of controller, the engine could overcome some drawbacks it terms of functioning characteristics.
Biodiesel/Jet-A mixtures have been fed to a piston aviation engine and several advantages occurred over the use of ethanol both in terms of physical-chemical properties and delivered performances. Moreover, gaseous pollutants concentrations decreased compared with the ones obtained from the use of classical aviation fuel. [
34,
35]
Other research papers examined the use of biodiesel as a sustainable fuel for small turbojet engines in laboratory conditions. The studies explore different types of biodiesels and JET-A-1 mixtures and assess their impact on the fundamental parameters of these engines. [
36]
The use of bio-ethanol as fuel for aviation turbine engines was also studied. Different compositions, specifically 5%, 10%, and 15% concentrations of bio-ethanol blended with Jet-A fuel, were subjected to testing using the JET CAT P80 micro-turbo-engine. Throughout the testing process, various parameters were meticulously monitored, including engine speed, thrust generated, temperature preceding the turbine, fuel volumetric flow rate, and vibration levels assessed in both axial and radial directions. The micro-turbo-engine was sustained at three distinct operational states: idle, cruise, and maximum speed, each lasting approximately 1 minute. Furthermore, a comparative evaluation was conducted between fuels, scrutinizing the micro-turbo-engine’s performance from the idle to maximum positions.
Upon completion of the tests, a comprehensive jet engine cycle analysis was carried out at the maximum operational state. This analysis involved the calculation of fuel-specific consumption, combustion chamber efficiency, and thermal efficiency of the engine for each fuel blend. It is pertinent to note that these assessments were executed without any alterations made to the engine components or the automation system. [
37]
In the field of power engineering, investigations into the impact of biofuels and alcohol-derived blends on gas turbines have been conducted. Elevated ethanol concentrations resulted in heightened carbon monoxide (CO) emissions. Conversely, nitrogen oxides (NOx) witnessed a substantial decrease of up to 70% in the presence of biofuels, and there was a concurrent reduction in particulate matter (PM10) [
38].
An analysis of the possibility of using recycled pork fat-based biodiesel as fuel for aviation turbo-engines is presented in [
39]. The analysis consists of the assessment of four blends of Jet-A kerosene with 10%, 30%, 50%, and 100% biodiesel. Current paper is basically a continuation of paper [
39].
The research conducted in this study provides an examination of the impacts associated with the utilization of biodiesel in a compact turbojet engine. The primary objective is to investigate the viability of a Jet-A and biodiesel blends as a potential fuel source for small turbojet engines, drawing upon insights from earlier research endeavours. The present study aims to evaluate the operational parameters of a micro turbo-engine commonly deployed in drones and aero-models. This assessment involves varying the composition of kerosene and biodiesel blends. Specifically, a comparative analysis was carried out, comparing fuel mixtures comprising Jet-A and 5% Aeroshell 500 Oil (Ke) against blends featuring 10%, 20%, and 30% biodiesel, with Ke serving as the benchmark reference point.
After determining the physical-chemical properties of the mixtures, a measurement campaign has followed where burning tests were made on the Jet Cat P80 micro-turbo-engine. The novelty of the paper compared with reference [
39] is that now the transitory regimes are taken into account and gaseous pollutants resulted from the combustion of the above-mentioned blends and regimes were assessed.
2. Materials and Methods
In order to establish the sustainability of fuel blends based on biodiesel, several investigations were performed within this paper. Thus, blends consisting of Jet-A aviation fuel (Ke), blends of Ke+10%BP, Ke+20%BP, Ke+30%BP.
Thus, within this chapter, experimental assessment of physical-chemical properties of the above-mentioned fuels and fuel blends will be performed. Also, functional testing will be made by feeding a micro turbo-engine with the above-mentioned fuels and fuel blends.
2.1. Blends Characterization
In this chapter are presented the equipment and the testing methods used to perform the determinations of the physical-chemical properties for the Jet-A fuel and Ethanol respectively all the fuel blends used for testing.
Density of the Fuel Blends Determination
Densities of: Jet-A fuel, BP and all tested fuel blends respectively, were measured as described in SR EN ISO 3675/2002 [
39]. The testing equipment is shown in
Figure 1.
Flash Point Measurements
Jet-A fuel, Ethanol and all tested fuel blends, had their flash point (the lowest temperature of which the substances’ vapours ignite in the presence of a flame) measured as described in ASTM D92 [
40].
Figure 2 is showing the Automatic flash point tester Cleveland, provided by Scavini, Italy used for this measurement.
Kinematic Viscosity Measurements
The measurements were made at 40°C, for the Jet-A fuel, Ethanol, respectively all tested fuel blends, was experimentally determined as described in SR EN ISO 3104/2002 [
41]. The equipment is shown in
Figure 3 and it’s provided by Scavini, Italy.
Low Calorific Power Determination
Low calorific power for the Jet-A fuel, Ethanol, respectively all tested fuel blends was experimentally determined accordance with ASTM D240-17 [
42]. IKA WERKE C 2000 Calorimeter provided by Cole-Parmer and shown in
Figure 4 was used to determine the low calorific power.
Elemental Analysis
An elemental analysis for the Jet-A fuel, Ethanol, respectively all tested fuel blends was made in order to assess the main elements of the fuels (C, N, H and O).
Percentage of carbon, hydrogen, nitrogen respectively oxygen content for the above-mentioned fuels have been determined as described in ASTM D 5291–16 [
43].
2.2. Theoretical Calculation of the Combustion Process
After the elemental composition of fuel blends was determined, their corresponding minimum air quantities required for stoichiometric combustion were calculated. The accurate calculation of resulting CO2 and water emissions allows a complete assessment of gaseous pollutant production during combustion. It was thus determined that the examined fuel blends generate lower levels of gaseous pollutants compared to conventional combustion processes.
2.3. Engine Experimental Procedure
The test bench, methods, equipment and testing procedure are presented in the following chapter. The experiments were performed on a Jet CAT P80® turbo-engine [
44], as shown in
Figure 6.
This chapter explores the impact of different fuel blends on the performance of a turbocharged engine. The investigated fuel blends consist of kerosene with varying percentages of biodiesel (10%BP, 20%BP, and 30%BP) and with 5% of Aeroshell 500 oil added to each blend for engine lubrication due to the fact that such a small engine does not have its own lubrication system. The tests were conducted under three distinct operating regimes: idle (18.7% throttle gas), cruise (30% throttle gas), and maximum (94% throttle gas for safety functioning). Each regime was subjected to a testing period of approximately 2 minutes, during which engine parameters were closely monitored. The measured parameters included temperature (Tcomp) after the compressor, temperature (Tcomb) before the turbine, fuel flow Qf, air flow, pressure in the combustion chamber, and thrust (F). The turbocharged engine maintained a constant shaft speed throughout the experiments, unaffected by the different fuel blends. However, to sustain this constant shaft speed, the fuel blends were introduced into the combustion chamber in varying proportions. Despite the variations in fuel blends, the compressor operated at a consistent speed, resulting in uniform pressure after the compressor and consistent air flow. Comparative assessments were made for parameters such as consumed fuel flow (Qf), temperature in front of the turbine (Tcomb), and thrust (F) under conditions of constant shaft speed.
2.4. Gaseous Emissions Measurements
The gaseous emission measurements were made by using the MRU Vario Plus analyser, which is presented in
Figure 7. Simultaneously, measurements of gas components (e.g., O
2, CO, NO, NO
2, NO
x, SO
2, and CH
4) are carried out.
4. Conclusions
The measurements made on Jet CAT P80® turbo-engine show that the addition of the biodiesel in fuel does not endanger the functionality of the turbo-engines.
A higher biodiesel concentration in blends will increase the freezing point which leads to the impossibility of using these blends at high altitudes without being heated. The calorific value decreases with the increase of the biodiesel concentration having as consequence the increase of the specific consumption.
Combustion temperatures in front of the turbines increase with the increase of biodiesel concentration without endangering the engine integrity. The combustion efficiency and the thermal efficiency of the engine do not show significant variations between the kerosene and the other mixtures.
The tests results presented in this paper showed that for all the studied cases, other than Jet-A fuel, the vibrations fit the limits of functionality, some regimes having slightly higher vibration levels. On the third regime presented, at a speed of around 80k RPM, the vibration levels are higher for the biodiesel blends that the Jet-A fuel. An explanation would be that the burn of biodiesel is causing a different temperature/pressure distribution on the turbine that produce an apparent unbalance.
The adding of biodiesel within the blends drastically decreases the gaseous emissions obtained from the combustion process. This is due to the fact that, on one hand BP brings more oxygen into the chemical formula and decreases the carbon content and, on the other hand it improved the combustion process and thus the need for outside air decreases.
Figure 1.
Fuels density measurement.
Figure 1.
Fuels density measurement.
Figure 2.
Automatic Flash Point Tester Cleveland.
Figure 2.
Automatic Flash Point Tester Cleveland.
Figure 3.
Kinematic viscosity determination equipment.
Figure 3.
Kinematic viscosity determination equipment.
Figure 4.
IKA WERKE C 2000 Calorimeter.
Figure 4.
IKA WERKE C 2000 Calorimeter.
Figure 5.
FTIR Spectrum OilExpress Series 100, v 3.0 spectrometer.
Figure 5.
FTIR Spectrum OilExpress Series 100, v 3.0 spectrometer.
Figure 6.
Engine setup for combustion experiments.
Figure 6.
Engine setup for combustion experiments.
Figure 8.
FTIR Spectra of the blends (Spectra of 100%BP - light green, spectra of 30%BP – dark green, spectra of 20%BP – red, spectra of 10% BP – blue, spectra of Ke – light blue).
Figure 8.
FTIR Spectra of the blends (Spectra of 100%BP - light green, spectra of 30%BP – dark green, spectra of 20%BP – red, spectra of 10% BP – blue, spectra of Ke – light blue).
Figure 9.
Rpm vs. time variation for starting procedure (until stable yield).
Figure 9.
Rpm vs. time variation for starting procedure (until stable yield).
Figure 10.
Tcomb vs. rpm and blends for starting procedure.
Figure 10.
Tcomb vs. rpm and blends for starting procedure.
Figure 11.
Qc (L/h) vs. rpm and blends for starting procedure.
Figure 11.
Qc (L/h) vs. rpm and blends for starting procedure.
Figure 12.
Tcomb vs. rpm during sudden acceleration and deceleration.
Figure 12.
Tcomb vs. rpm during sudden acceleration and deceleration.
Figure 13.
Qc (L/h) vs. rpm during sudden acceleration and deceleration.
Figure 13.
Qc (L/h) vs. rpm during sudden acceleration and deceleration.
Figure 14.
F vs. rpm during sudden acceleration and deceleration.
Figure 14.
F vs. rpm during sudden acceleration and deceleration.
Figure 15.
Variation of T3 (°C) depending on regime and blends.
Figure 15.
Variation of T3 (°C) depending on regime and blends.
Figure 16.
Variation of Qc [L/h] depending on the regime and blend.
Figure 16.
Variation of Qc [L/h] depending on the regime and blend.
Figure 17.
Variation of thrust F[N] depending on the regime and blend.
Figure 17.
Variation of thrust F[N] depending on the regime and blend.
Figure 18.
CO concentration vs. regimes and blends.
Figure 18.
CO concentration vs. regimes and blends.
Figure 19.
SO2 concentration vs. regimes and blends.
Figure 19.
SO2 concentration vs. regimes and blends.
Figure 20.
NOx concentration vs. regimes and blends.
Figure 20.
NOx concentration vs. regimes and blends.
Figure 21.
Variation of specific consumption for all the tested fuel blends.
Figure 21.
Variation of specific consumption for all the tested fuel blends.
Figure 22.
Variation of the combustion efficiency for all the tested fuel blends for 3 regimes.
Figure 22.
Variation of the combustion efficiency for all the tested fuel blends for 3 regimes.
Figure 23.
Variation of the thermal efficiency for all the tested fuel blends for maximum regime.
Figure 23.
Variation of the thermal efficiency for all the tested fuel blends for maximum regime.
Table 1.
Obtained results of the physical-chemical determinations.
Table 1.
Obtained results of the physical-chemical determinations.
Sample |
Flash Point [°C] |
Viscosity at 40°C, [cSt] |
Density at 22°C, [g/cm3] |
Low Calorific Value, [kJ/kg] |
Elemental analysis, [%] |
Ke |
42.3 |
1.39 |
0.817 |
45.292 |
C% = 85.17 H% = 13.31 N% = 0.07 O% = 1.45 |
Ke+10%BP |
44.2 |
1.51 |
0.823 |
44.403 |
C% = 84.40 H% = 13.22 N% = 0.07 O% =2.32 |
Ke+20%BP |
50.2 |
1.82 |
0.830 |
43.67 |
C% = 83.21 H% = 13.1 N% = 0.07 O% =3.62 |
Ke +30%BP |
54.7 |
2.06 |
0.836 |
41.99 |
C% = 82.85 H% = 13.03 N% = 0.07 O% =4.05 |
100% BP |
161 |
5.08 |
0.875 |
39.323 |
C% = 77,43 H% = 12,38 N% = 0,06 O% = 10,13 |