1. Introduction
Since wind and solar power sources are intermittent in nature and are generally far from urban centers, there is a compelling need to store large quantities of renewable energy with a faster response. The popular power from hydrogen concept via a water splitter can be used to create ammonia by reacting hydrogen with nitrogen in an air separation unit (ASU). Ammonia is currently manufactured at a large scale as an industrial chemical and fertilizer. Owing to its various merits—ammonia (1) is easy to store as a liquid; similar to propane; (2) has a high energy density; and (3) handling experience and infrastructure are already available—nowadays, ammonia is widely considered as an important hydrogen-carrier for future marine shipping or commercial aviation to drive turbines or engines,
Figure 1. Ammonia can be easily cracked back to pure hydrogen for those applications that use pure hydrogen or a mix of hydrogen with other fuels, including ammonia itself [
1,
2,
3,
4,
5,
6].
However, through fuel NOx mechanisms, nitrogen-containing ammonia can lead to significant NOx emissions. Further, there are also concerns about unburnt ammonia and slow ammonia kinetics at low temperatures. On the other hand, using natural gas (NG) as a fuel has distinct advantages, such as
- (1)
Higher hydrogen content relative to gasoline, diesel, and coal;
- (2)
High adiabatic flame temperature and high laminar flame speed;
- (3)
Well-established infrastructure;
- (4)
Abundance of natural gas reserves in the US.
- (5)
A worldwide increase in liquefied natural gas (LNG) plants and terminals.
Because of the above-mentioned advantages, cofiring ammonia with natural gas has gained significant attention as a clean source of energy in gas turbines for power generation as well as in internal combustion engines (ICE) for transportation. Even though cofiring ammonia with natural gas can ease the above-mentioned emission concerns of combusting ammonia alone, additional emissions, such as soot, carbon monoxide, unburnt hydrocarbons, and Volatile Organic Compounds (VOCs), still need to be addressed [
7,
8,
9,
10,
11,
12,
13,
14,
15,
16,
17,
18,
19].
There are full mechanisms in the literature that address combustion involving ammonia in the air. The detailed Konnov mechanism for ammonia consists of 129 species and 957 reactions [
11]. A new version of the Konnov model targeting the ammonia flame and an improved hydrocarbon subset has also been reported [
13,
14]. The CEU-NH
3 mechanism for ammonia and methane/methanol/ethanol contains 91 species and 444 reactions [
15]. The UC San Diego mechanisms are a suite of mechanisms, including nitrogen and hydrocarbon-based chemistry [
16]. The USCII full mechanism, developed by Professor Hai Wang, is a detailed kinetic mechanism tailored for hydrogen and C
1 to C
4 combustion with 111 species in 784 reversible reactions [
17,
18,
19].
The objective of this study is to develop a reaction mechanism that can be used in computational fluid dynamics’ (CFD) modeling to predict NOx/soot/unburnt NH
3/unburnt hydrocarbons/volatile organic compound (VOC) emissions under gas turbine and internal combustion engine (ICE) conditions. The Konnov and the USCII mechanisms [
10,
17,
18,
19] were combined to become the full mechanism (Modified Konnov Mechanism). The full Konnov mechanism has 129 species. Additional species (C
4H
10, pC
4H
9, and nC
3H
7) and associated mechanisms from USCII were added to the Konnov mechanism to make the Modified Konnov Mechanism, which has 132 species and 1238 reactions.
Reduced mechanisms are required for practical turbine/ICE applications due to the complexity of 3D computational fluid dynamics’ (CFD) simulations. The CFD simulations are widely used in turbine, engine, and furnace design for analyzing flame stability, autoignition zone, temperature/velocity profiles, fuel/oxidizer mixing patterns, and emission rates. However, coupling detailed reaction mechanisms with momentum, heat, mass transport equations, and stiff differential equations proved to be a serious burden on computational speed and numerical convergence. Thus, it is imperative to adopt reduced mechanisms not only for saving computer storage and running time but also for numerical convergence for practical applications. For instance, ANSYS Fluent sets the maximum number of species in the reactions to 50. One of the goals of this paper is to contribute an ammonia–methane cofiring reduced mechanism that can handle heavier hydrocarbons (C
2 and C
3) in natural gas streams,
Table 1. Further, many existing reduced mechanisms for ammonia and methane mixtures are unsuitable for predicting soot emissions. Therefore, the developed reduced mechanism NH
3NG also included soot precursor species C
2H
2 and C
2H
4 to facilitate soot emission estimation. NH
3NG compares well with the full mechanism and existing reduced mechanisms when validated against experimental ignition delay, adiabatic temperature, laminar flame speed, and NOx/CO emissions [
20,
21,
22,
23,
24,
25,
26,
27,
28,
29,
30,
31,
32,
33].
4. Discussion
Even though the mechanism reduction with Chemkin was conducted at a temperature of 1500 K and pressure of 300 bar for the purpose of developing a reduced mechanism that is useful for high-efficiency turbine and engine applications, the reduced mechanism NH
3NG did remarkably well in validation at a wide range of experimental conditions, including those conducted at lower temperatures and pressures (e.g., laminar flame speed data at 423 K and 1–3 atm. [
28] and ignition delay data at 16 atm. and 1227–1307 K [
36]).
The Moss–Brookes model for soot prediction is applicable to higher hydrocarbon species (ethane and propane) by including appropriate soot precursors and participating surface growth species. In our earlier work of the LU 3.0.1 reduced mechanism for combustion of C
1 to C
4 light hydrocarbons, three precursor and surface growth species C
2H
2, C
2H
4, and C
6H
6, were involved. In this work, due to the limitation of the number of species and the addition of ammonia fuel, only two soot precursor species, C
2H
2 and C
2H
4, were included in NH
3NG. However, these two precursor/surface growth species were deemed sufficient to predict soot emission because even if neither is present, curve fitting can be used in Fluent to determine the precursor and surface growth species’ mass fractions [
37,
38,
39,
40].
The reactor used in Rocha et al.’s 2019 experiments [
9] was a porous media flat burner type, while in the Chemkin simulation, the available types were the batch, constant volume, constant pressure reactor, perfectly/partially stirred, and plugged flow reactors. In our predictions, we assumed an equilibrium (adiabatic) perfectly stirred reactor for simplicity. However, NH
3NG predictions still largely agreed with the literature values. Another feature that differentiates our work from other literature mechanisms (i.e., those shown in
Figure 7 and
Figure 8) is that the full mechanism (the Modified Konnov Mechanism, 132 species and 1238 reactions) used in this work was a combination of Konnov’s mechanism and the USCII mechanism, while others are in the family of the Konnov mechanism for ammonia/methane combustion. NH
3NG allowed the simulation of heavier hydrocarbons, such as ethane and propane, and also had a better capability to predict soot emission with soot precursors C
2H
2 and C
2H
4 using the Moss–Brookes’ equation in ANSYS Fluent [
38,
39].
In future work, NH
3NG can be used in ANSYS Fluent CFD simulations to further study the combustion process. For example, 3-D CFD simulations for various types of low NOx and 2-stage burners that are suitable for modern gas/supercritical-CO
2 turbines and ICE applications can be performed [
43,
44]. NOx/soot/CO/unburnt fuel/VOC emissions under various equivalence ratios, NH
3 to NG, NG composition, fuel flow rate, and air/fuel mixing patterns, can be estimated using ANSYS Fluent. CFD features, such as lean blow-off (LBO), can be used to investigate injection patterns and flame stability [
46].
The developed NH3NG Chemkin files are available from the corresponding author upon request.
5. Conclusions
A fuel mixture of ammonia and natural gas provides clean, low-carbon energy to run gas turbines and internal combustion engines for power generation, railroad/truck transportation, marine shipping, and commercial aviation. Reduced mechanisms are required in certain CFD software and can save computer time and storage in others for 3D CFD combustion applications. The newly proposed NH3NG reduced mechanism can be employed in CFD works for the prediction of NOx, CO, and soot emissions involving ammonia and natural gas combustion. Soot emission can be predicted by applying the Moss–Brookes–Hall model using soot precursor species.
The prediction errors for NOx and CO emissions associated with the use of the NH3NG mechanism for ammonia–natural gas mixtures were also minimal (abs. error 5%) in comparison to the full Modified Konnov mechanism (a combination of the Konnov mechanism and the USCII mechanism). The NH3NG reduced mechanism was validated with experimental laminar flame speed, ignition delay, adiabatic temperature, and NOx and CO emissions’ data.
The effect of ammonia in such fuel mixtures was also analyzed by comparing the Laminar flame speeds of the reduced mechanism to values found in the literature. An increase in the ammonia concentration in such a fuel mixture decreased the laminar flame speed of the combustion flame. An average absolute error of 7.7% was obtained for the laminar flame speed prediction, which is well within the reported experimental uncertainty of 10% [
28]. The R
2 between prediction and data was 0.985. The ignition delay time of the NH
3NG mechanism also agrees with the experimental data found in literature. An increase in the ammonia concentration in such a fuel mixture increased the ignition delay of the combustion flame. An average ignition delay prediction error of 13% was also within typical experimental data uncertainties (10–20%). The predictions of adiabatic temperatures were within 1 °C. Similar to all mechanisms in the literature, the present work overpredicted NOx and CO emissions in relation to the published data [
9,
16,
20,
21]. Overall, the predictions from the NH
3NG mechanism are in line with other literature mechanisms. Compared to other mechanisms in the literature, the predicted CO emissions from NH
3NG were higher (further from the experimental data), while the predicted NOx emissions were lower (closer to the experimental data).