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Article

Reduced Mechanism for Combustion of Ammonia and Natural Gas Mixtures

1
Flutura, 5858 Westheimer Suite 405, Houston, TX 77057, USA
2
John Zink Hamworthy Combustion, 11920 E Apache St., Tulsa, OK 74116, USA
3
Dan F. Smith Department of Chemical Engineering, Lamar University, Beaumont, TX 77710, USA
*
Author to whom correspondence should be addressed.
Clean Technol. 2023, 5(2), 484-496; https://doi.org/10.3390/cleantechnol5020025
Submission received: 11 October 2022 / Revised: 10 March 2023 / Accepted: 10 April 2023 / Published: 12 April 2023
(This article belongs to the Special Issue Green and Sustainable Chemistry for Energy Application)

Abstract

:
A fuel mixture of ammonia and natural gas as a low-carbon alternative for future power generation and transportation is an attractive option. In this work, a 50-species reduced mechanism, NH3NG, suitable for computational fluid dynamics simulations (CFD), is developed for ammonia–natural gas cofiring while addressing important emission issues, such as the formation of nitrogen oxides (NOx), soot, carbon monoxide, and unburnt methane/ammonia. The adoption of reduced mechanisms is imperative not only for saving computer storage and running time but also for numerical convergence for practical applications. The NH3NG reduced mechanism can predict soot emission because it includes soot precursor species. Further, it can handle heavier components in natural gas, such as ethane and propane. The absolute error is 5% for predicting NOx and CO emissions compared to the full Modified Konnov mechanism. Validation with key performance parameters (ignition delay, laminar flame speed, adiabatic temperature, and NOx and CO emissions) indicates that the predictions of the reduced mechanism NH3NG are in good agreement with published experimental data. The average prediction error of 13% for ignition delay is within typical experimental data uncertainties of 10–20%. The predicted adiabatic temperatures are within 1 °C. For laminar flame speed, the R2 between prediction and data is 0.985. NH3NG over-predicts NOx and CO emissions, similar to all other literature methods, but the NOx predictions are closer to the experimental data.

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-NH3 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 C1 to C4 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 NH3/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 (C4H10, pC4H9, and nC3H7) 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 (C2 and C3) 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 NH3NG also included soot precursor species C2H2 and C2H4 to facilitate soot emission estimation. NH3NG 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].

2. Methodology

The mechanism reduction was performed using Chemkin 2019 R2 [33,34,35,36]. The following steps were taken to determine the 50 species to be included in the reduced mechanism NH3NG:
  • The species in the reduced mechanism should be suitable for the targeted applications in turbine/engine design with CFD. In this study, the reduced mechanism should include fuel species, emission species (NO, NO2, NH3, HCN, N2O), and soot precursors (C2H2, C2H4).
  • The next step is to utilize the Reaction Path Analyzer (RPA) tool in Chemkin. RPA provides a visualization of the inner relationships of the chemistry model, as shown in Figure 2.
  • The final step in species selection is to apply the Reaction Rate Analysis (RRA) tool. In this Chemkin analysis, the Perfectly Stirred Reactor (PSR) model is adopted. In these PSR runs, the species with a higher rate of production or destruction are expected to be dominant in the reaction mechanism and, thus, are ranked higher. Both RPA and RRA are needed to identify important intermediate species for NH3NG to represent the essential elements of the full Modified Konnov Mechanism.

2.1. Preliminary Species Selection

Mechanism reduction was conducted at a temperature of 1500 K and pressure of 300 bar, using Chemkin 2019 R2 [36]. For the reduced mechanism, the initial species list included Fuel Species (NH3, CH4, C2H6, C3H8), NOX and NOy (NO, NO2, HONO), Soot Precursors (C2H2, C2H4), and Air (O2, N2, Ar).
The soot precursor species C2H2 and C2H4 are important in that the soot emission can be predicted with precursor-based soot models, such as the Moss–Brookes’ equation (with the built-in Fenimore–Jones soot oxidation model) listed in ANSYS Fluent [26,27,28,29,30,31,32]. Additional species (C, CH, CH2, C3H3, and C4H4) were also included as they were part of the reaction intermediates.

2.2. Reaction Path Analyzer (RPA)

The reaction path analyzer (RPA) displays reaction pathways connecting the species. Since the path width is proportional to its rate of production, RPA helps identify the main intermediates during reactions and eliminates any species with negligible contributions [28]. In this study, reaction paths between fuel components and the major intermediates/products (CO, CO2, NO, NO2, C2H4) were analyzed. The major contributing reactions and participating species were identified. Figure 2 shows the reaction pathways for CO production.

2.3. Reaction Rate Analysis (RRA)

The important intermediate species were selected based on the active participation of the species in the reaction. To determine the key intermediate species, the production and destruction rates were added and sorted to obtain the ranks of the species. The species with a higher rate of production or destruction were ranked higher. From the rankings list, it was observed that most of the species were already included in the reduced mechanism. However, some species, such as C, CH, CH2, C3H3, and C4H4, were still needed (e.g., for soot production). Therefore, they were subsequently added to the list, and the mechanism was reduced further. Figure 3 gives the reaction rate analysis for the key intermediate C2H4, a soot precursor species. Table 2 shows the final 50 selected species.

3. Results

3.1. Comparison with the Full Mechanism

The new reduced mechanism was compared against the full modified Konnov mechanism at a residence time of 1 s and ignition temperature of 1500 K, and pressure of 300 bar. The predicted mole fractions of the important combustion products obtained from the Chemkin simulation of the reduced mechanism at various residence times were recorded. Table 3 summarizes the prediction errors at a 1 s residence time for an ammonia–methane mixture. The predicted mole fraction differed from the full Modified Konnov Mechanism mole fractions by an average absolute error of 1.90 × 10−6 for the major species.
The average absolute % error of 5.44% between the NH3NG reduced mechanism and modified Konnov full mechanism is reasonable, considering the goals of NH3NG are to accommodate soot prediction and to handle C2-C3 hydrocarbon species. All in all, NH3NG offers a simple mechanism (with 50 species) suitable for CFD applications. The larger absolute % error of 11.79% for NH3 represents the compromise between the original Konnov mechanism designed for NH3 combustion and the USC II mechanism designed for hydrocarbon combustion.

3.2. Validation with Experimental Data

The 50 species reduced mechanism for ammonia–natural gas cofiring NH3NG was validated against key experimental performance indicators such as laminar flame speed, ignition delay, adiabatic temperature, and NOx and CO emissions [16,20,21]. The reduced mechanism containing 50 species and reactions, along with the thermodynamics file, was preprocessed using the Chemkin-Pro preprocessor. The validated reduced mechanism, NH3NG, can then be used in other ANSYS FLUENT CFD simulations [20,21,22,23,24,25,26,27,28,29,30,31,32,33,34,35,36,37,38,39,40,41,42,43,44,45,46].

3.2.1. Laminar Flame Speed

Flame speed is a fundamental property of the fuel–air mixture that influences the design of combustion equipment. Laminar flame speed is the speed at which a laminar flame propagates through a pre-mixture of fuel and air. The flame speed depends on the properties of the fuel mixture and the thermodynamic conditions, such as temperature and pressure, when ignited.
The flame speed calculation model in Chemkin was used to evaluate the performance of the reduced mechanism against the experimental values of the NH3/CH4/air system found in Rocha et al. [20]. The experimental results were used to validate the mechanism for different mixtures of ammonia and methane in the air. During validation, the temperature and pressure inside the reactor were set at 423 K and 1–3 atm., respectively. The equivalence ratio varied between 0.8 and 1.2 for all fuel mixtures. The ammonia blending fractions in the binary fuel mixtures were also varied, as shown in Table 4. The equivalence ratio is defined as the ratio of the actual fuel/oxidizer ratio to the fuel/oxidizer ratio in the stoichiometric equation. Many properties of combustion processes strongly depend on the stoichiometry of the combustion mixture. Table 4 shows an average absolute error of 7.7%, which is well within the reported experimental uncertainty of 10% [28]. As shown in Figure 4, the predicted results from the NH3NG mechanism agreed with the experimental data very well, with an R2 = 0.985.

3.2.2. Ignition Delay

The period between the creation of a combustible mixture when the fuel is injected into an oxidizing environment and the sustained onset of the rapid reaction phase leading to a rise in temperature and pressure is defined as the ignition delay time. For ignition delay time calculations, a closed homogeneous reactor model was used. The reduced mechanism was compared against the experimental data from J. Huang et Al. [30]. For validation in Chemkin, the pressure was taken as 16 atm. and the temperature varied between 1227 and 1307 K. The fuel composition was CH4/C2H6/O2/N2 (8.93–0.34–19.05–71.68%). Table 5 shows the numerical comparison between the predictions and lab data with an average absolute error of 13%, which is well within the combined temperature/concentration uncertainties (8%) [30] and typical experimental data uncertainties (10–20%) [33]. Figure 5 shows the graphical representation of the experimental and simulation results between ignition delay time and for the said mixture with the new mechanism at the conditions mentioned above.

3.2.3. Adiabatic Temperature

The adiabatic flame temperature is the maximum temperature when a particular gas mixture reaches equilibrium under an adiabatic combustion condition. In a real system, due to heat losses and chemical kinetic/mass transport limitations, the flame temperature is likely to be lower. In this validation, the adiabatic temperature was estimated with the Chemkin equilibrium model. The inlet composition of fuel and air mixtures was set at 0.8 equivalence ratios. The initial temperature and pressure were set at 293 K and 1 atm., respectively, for both fuel and air. An adiabatic flame temperature comparison of the Chemkin simulation and experimental data for ammonia and methane flames at different mole fractions of NH3 is shown in Figure 6 and Table 6 [9]. As seen in Table 6, the predictions were right on target, which indicates the quality of the thermodynamic properties used in the NH3NG mechanism.

3.2.4. NOx and CO Emissions

In this section, we compared the predicted NOx and CO emissions from NH3NG reduced mechanism with the experimental emission data, as well as those from different mechanisms in the literature [9,16,20,21]. These reactions were carried out in an adiabatic reactor with different CH4/NH3 ratios, as shown in Table 6. The NOx and CO measurements and predictions for a thermal input of 1200 W and an equivalence ratio of 0.8 are shown in Figure 7 and Figure 8.
As shown in Figure 7 and Figure 8, all mechanisms, including the present work, over-predict NOx and CO emissions in relation to the published data available [9,16,20,21]. Overall, the predictions from the NH3NG mechanism were in line with other literature mechanisms. Compared to other mechanisms in the literature, the predicted CO emissions from NH3NG were higher (further from the experimental data). In comparison, the predicted NOx emissions were lower (closer to the experimental data).

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 NH3NG 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 C1 to C4 light hydrocarbons, three precursor and surface growth species C2H2, C2H4, and C6H6, 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, C2H2 and C2H4, were included in NH3NG. 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, NH3NG 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. NH3NG allowed the simulation of heavier hydrocarbons, such as ethane and propane, and also had a better capability to predict soot emission with soot precursors C2H2 and C2H4 using the Moss–Brookes’ equation in ANSYS Fluent [38,39].
In future work, NH3NG 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-CO2 turbines and ICE applications can be performed [43,44]. NOx/soot/CO/unburnt fuel/VOC emissions under various equivalence ratios, NH3 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 R2 between prediction and data was 0.985. The ignition delay time of the NH3NG 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 NH3NG mechanism are in line with other literature mechanisms. Compared to other mechanisms in the literature, the predicted CO emissions from NH3NG were higher (further from the experimental data), while the predicted NOx emissions were lower (closer to the experimental data).

Author Contributions

A.R.K. performed the literature review, validation of the reduced mechanism, and writing. V.D.D. contributed to the reduction of the full Modified Konnov Mechanism to NH3NG. D.H.C. worked on the discussion, conclusion, and writing. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by the Texas Air Research Center (TARC Grant #110LUB0179A). TARC was not involved in study design, in the collection, analysis, and interpretation of data, in the writing of the report, and in the decision to submit the article for publication.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

Glossary

ICEInternal Combustion Engines
NGNatural Gas
LNGLiquified Natural Gas
VOCVolatile Organic Compound
CFDComputational Fluid Dynamics
RPAReaction Path Analyzer
PSRPerfectly Stirred Reactor

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Figure 1. Ammonia energy density chart [3].
Figure 1. Ammonia energy density chart [3].
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Figure 2. Reaction path analyzer (RPA) for the production of CO with the line thickness proportional to the rate of reactions.
Figure 2. Reaction path analyzer (RPA) for the production of CO with the line thickness proportional to the rate of reactions.
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Figure 3. Reaction rate analysis of C2H4.
Figure 3. Reaction rate analysis of C2H4.
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Figure 4. Laminar flame speed predictions from NH3NG reduced mechanism vs. experimental data.
Figure 4. Laminar flame speed predictions from NH3NG reduced mechanism vs. experimental data.
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Figure 5. Ignition delay time predictions vs. experimental data [30].
Figure 5. Ignition delay time predictions vs. experimental data [30].
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Figure 6. Adiabatic temperature (experimental vs. NH3NG reduced mechanism) [9].
Figure 6. Adiabatic temperature (experimental vs. NH3NG reduced mechanism) [9].
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Figure 7. Comparison of NOx emission predictions versus NOx measurements for a thermal input of 1200 W and equivalence ratio of 0.8 [9,16,20,21].
Figure 7. Comparison of NOx emission predictions versus NOx measurements for a thermal input of 1200 W and equivalence ratio of 0.8 [9,16,20,21].
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Figure 8. Comparison of CO emission predictions versus CO data for a thermal input of 1200 W and equivalence ratio of 0.8 [9,16,20,21].
Figure 8. Comparison of CO emission predictions versus CO data for a thermal input of 1200 W and equivalence ratio of 0.8 [9,16,20,21].
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Table 1. Natural gas composition [4].
Table 1. Natural gas composition [4].
ComponentTypical (%)Range (Mole)
Methane94.987.0–96.0
Ethane2.51.8–5.1
C3+0.30.1–2.3
Nitrogen 1.61.3–5.6
Carbon0.70.1–1.0
Table 2. Fifty (50) species of the NH3NG combustion mechanism.
Table 2. Fifty (50) species of the NH3NG combustion mechanism.
50 SpeciesAr N2 H H2 O O2 OH HO2 H2O CO CO2 HCO CH3 CH4 C2H6 CH2O C2H5 CH2 CH3O CH2OH CH C2H2 C2H4 C2H3 CH3OH CH2CO HCCO C CH2HCO NH NO NCO N2O NH2 HNO NO2 NNH NH3 HONO CNN H2NO C3H6 C3H8 iC3H7 nC3H7 C3H3 C3H5 C3H4 C4H4 iC4H3
Table 3. Comparison of prediction errors of reduced mechanisms for the mole fraction of the major species at a residence time of 1 s for CH4-NH3 fuel.
Table 3. Comparison of prediction errors of reduced mechanisms for the mole fraction of the major species at a residence time of 1 s for CH4-NH3 fuel.
SpeciesKonnov (Modified)NH3NGAbsolute ErrorAbsolute % Error
CH44.85 × 10−75.34 × 10−71.10122 × 10−99.99
NH31.59 × 10−61.78 × 10−61.8799 × 10−711.79
CO 5.14 × 10−65.51 × 10−63.6462 × 10−77.09
CO26.06 × 10−26.06 × 10−23 × 10−70
H21.37 × 10−71.46 × 10−79.101 × 10−96.65
NO21.34 × 10−51.37 × 10−52.315 × 10−71.72
HNO2.84 × 10−92.82 × 10−91.612 × 10−110.57
NO2.48 × 10−42.34 × 10−41.41 × 10−55.69
Average 1.90 × 10−65.44
Table 4. Laminar flame speed predictions versus experimental data of NH3/CH4/air system [28].
Table 4. Laminar flame speed predictions versus experimental data of NH3/CH4/air system [28].
Sr. No.Pressure (Bar)xNH3Equivalence RatioExperimental (cm/s)NH3NG (cm/s)Error (%)
130.20.826.626.60.1%
210.2151.851.80.0%
320.2141.642.62.5%
430.2135.737.34.5%
510.21.243.245.86.0%
620.21.233.337.111.5%
730.21.227.931.914.3%
830.41.223.626.512.2%
930.61.219.322.014.0%
1030.81.216.418.412.4%
Avg. 7.7%
Table 5. Ignition delay time predictions versus experimental data of NH3/CH4/air system [21].
Table 5. Ignition delay time predictions versus experimental data of NH3/CH4/air system [21].
8.93% CH4, 0.34% C2H6 Mixture
Pressure (atm)Temp (K)1000/TIgnition Time NH3NG (s)Ignition Time Experimental (s)Absolute ErrorAbsolute Error %
16.313070.765113.15 × 10−43.83 × 10−46.85 × 10−518%
15.812710.786784.67 × 10−45.28 × 10−46.15 × 10−512%
16.212270.8157.52 × 10−46.92 × 10−46.03 × 10−59%
Average 13%
Table 6. Comparison of adiabatic temperature predictions and data [9].
Table 6. Comparison of adiabatic temperature predictions and data [9].
Fuel MixtureNH3 Mole FractionInitial Temperature (K)Adiabatic Temperature Exp. Data (°C) [7]Adiabatic Temperature Prediction (°C)
NH3/CH40.329316981698.4
0.529316791678.8
0.729316511651.6
0.829316341633.7
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Khade, A.R.; Damodara, V.D.; Chen, D.H. Reduced Mechanism for Combustion of Ammonia and Natural Gas Mixtures. Clean Technol. 2023, 5, 484-496. https://doi.org/10.3390/cleantechnol5020025

AMA Style

Khade AR, Damodara VD, Chen DH. Reduced Mechanism for Combustion of Ammonia and Natural Gas Mixtures. Clean Technologies. 2023; 5(2):484-496. https://doi.org/10.3390/cleantechnol5020025

Chicago/Turabian Style

Khade, Aniket R., Vijaya D. Damodara, and Daniel H. Chen. 2023. "Reduced Mechanism for Combustion of Ammonia and Natural Gas Mixtures" Clean Technologies 5, no. 2: 484-496. https://doi.org/10.3390/cleantechnol5020025

APA Style

Khade, A. R., Damodara, V. D., & Chen, D. H. (2023). Reduced Mechanism for Combustion of Ammonia and Natural Gas Mixtures. Clean Technologies, 5(2), 484-496. https://doi.org/10.3390/cleantechnol5020025

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