Open Access Article
Anantha Krishnan Vinayak
Soman
,
Siqi
Wang
*,
Ziqi
Shen
and
Mingming
Zhu
Faculty of Engineering and Applied Sciences, Cranfield University, Bedford, MK43 0AL, United Kingdom. E-mail: siqi.wang2019@cranfield.ac.uk
First published on 31st October 2025
In this study, a novel chemical looping ammonia cracking (CLCr) process was designed for efficient hydrogen production. A closed-loop, three-reactor chemical looping system using iron oxide as the oxygen carrier was modelled in Aspen Plus. A parametric study was carried out to evaluate the effect of key parameters, including the air reactor outlet temperature, fuel reactor outlet temperature, ammonia to oxygen carrier ratio, and the steam reactor pressure. The optimal operating conditions were then identified, under which a hydrogen yield of 69.4% with 99.99% purity can be achieved with an overall energy efficiency of 79.6%. An energy balance analysis was also carried out to confirm that the process is autothermal, and the overall exergy efficiency of the process was 70.4%. These findings highlight the novel CLCr process as an energy-efficient alternative to conventional ammonia catalytic cracking for hydrogen production.
As a hydrogen carrier, ammonia needs to be converted back to hydrogen at the end-use point. Currently, the predominant pathway to convert ammonia into hydrogen is through thermocatalytic ammonia cracking. One of the limitations of this process is that the reaction is highly endothermic (46 kJ mol−1 NH3) with additional energy required for liquid ammonia vaporisation (23.4 kJ mol−1) and preheating (liquid ammonia heat capacity of 50 J mol−1 K−1).5 Moreover, of all the catalysts tested for the reaction, Ru-based catalysts remain the performance benchmark, limiting the scalability of the process due to their cost. Although non-noble metal-based and bimetallic alternatives have been studied, the reaction temperature required for these catalysts to reach a desirable reaction rate remains high.6,7 Aside from the kinetics and catalyst limitations, an inherent challenge of the process is the extensive purification process required for the reactor off-gas, which contains a 1
:
3 molar ratio mixture of N2 to H2 with unreacted NH3, to produce a high-purity hydrogen stream.
The Chemical Looping (CL) technology provides a suitable option to address the challenges faced by conventional thermocatalytic ammonia cracking. CL has been extensively studied for hydrogen production from methane and other hydrocarbon fuels.8–12 In addition, the CL process can be integrated with renewable energy and bio-feedstocks to improve energy efficiency and reduce carbon emission. For example, solar-assisted chemical looping systems have been proposed to combine redox cycles with concentrated solar energy, significantly improving hydrogen yield while reducing emissions.13 CO2-rich waste gases, such as landfill gases, have also been explored as alternative feedstocks for syngas production, offering a sustainable route for both hydrogen production and CO2 utilisation.14
A typical three-reactor CL process involves three main steps: (1) the reactions between the fuel and the oxygen carrier (metal oxides) to produce carbon dioxide in the Fuel Reactor (FR); (2) the reactions between the reduced oxygen carrier and steam to produce hydrogen in the Steam Reactor (SR); (3) the reaction between the oxygen carrier and air to regenerate the oxygen carrier and produce an oxygen-depleted N2 stream in the Air Reactor (AR).
In this study, a closed-looped three-reactor CL process for ammonia cracking is conceptualised, named as Chemical Looping Ammonia Cracking (CLCr), where iron oxide is used as the oxygen carrier to crack ammonia and produce ultra-high purity hydrogen. Iron oxide was selected as the oxygen carrier (OC) due to its abundance, thermal stability, and low cost.15 In the chemical looping reforming (CLR) process, iron oxides also showed good reactivity, high oxygen adsorption capacity, and high resistance against sintering.16,17 Recent studies on iron ore direct reduction using ammonia suggest that it is feasible to use iron oxides as an oxygen carrier for ammonia reduction.18,19 Furthermore, experimental thermogravimetric analyses reported by Ma et al. showed that Fe2O3 can be fully reduced under NH3 at 700 °C without the formation of NOx,20 confirming its reducibility under ammonia-rich environment. In addition, metallic Fe – formed upon complete reduction of iron oxides – has been demonstrated to be active for ammonia decomposition.21 These experimental findings are consistent with the reaction pathways considered in this work, providing confidence in the feasibility of the proposed process. This work aims to design a CLCr process via Aspen Plus modelling and evaluate the effect of key process parameters on the performance of the system through a parametric analysis. Finally, a process was developed using the optimal operation conditions identified in the parametric analysis and the thermodynamic analysis was carried out on the optimised process.
| Name | Type | Component name | Databank |
|---|---|---|---|
| Fe2O3 | Solid | Hematite | APV121.PU |
| Fe3O4 | Solid | Magnetite | APV121.SOLIDS |
| Fe0.947O | Solid | Wustite | APV121.INORGANIC |
| Fe | Solid | Iron | APV121.PURE39 |
| Al2O3 | Solid | Alumina | APV121.PURE39 |
| Fe4N | Solid | Iron nitride | APV121.INORGANIC |
| NH3 | Conventional | Ammonia | APV121.PURE39 |
| N2 | Conventional | Nitrogen | APV121.PURE39 |
| H2 | Conventional | Hydrogen | APV121.PURE39 |
| O2 | Conventional | Oxygen | APV121.PURE39 |
| H2O | Conventional | Water | APV121.PURE39 |
| NO2 | Conventional | Nitrogen dioxide | APV121.PURE39 |
| NO | Conventional | Nitric oxide | APV121.PURE39 |
| N2O | Conventional | Nitrous oxide | APV121.PURE39 |
| Subjects | Selection | References |
|---|---|---|
| Properties | ||
| Property method | PR-BM | 28–31 |
| Steam class | MIXCISLD | 32 |
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| Unit operation blocks | ||
| Reactors | RGibbs | 30, 31, 33 and 34 |
| Heat exchangers | HeatX | 35 |
| Heaters | Heater | 28 |
| Pressure changers | Compr, valve | 28 |
| Separators | Flash2 | 28 |
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| Assumptions | ||
| Ambient conditions | 1 atm, 25 °C | 34 |
| Pressure drops | Zero | 30, 33 and 36–38 |
| Air | 79 mol% N2, 21 mol% O2 | 28, 34 and 39 |
| Minimum approach temperature (MAT) of heat exchangers | 10 °C | 34, 40 and 41 |
| Minimum approach temperature (MAT) of steam generator | 10 °C | 34, 40 and 41 |
| Minimum approach temperature (MAT) of ammonia vaporiser | 3 °C | 41 |
| Isentropic efficiency-compressor | 89% | 34 and 42 |
| Mechanical efficiency-compressor | 97% | 34 and 40 |
| Pump efficiency | 90% | 34 and 40 |
| Isentropic efficiency-turbine | 93% | 34 and 42 |
| Mechanical efficiency-turbine | 96.6% | 40 and 42 |
| Generator efficiency | 99% | 43 |
| Reactors of FR, AR and SR | Adiabatic, Gibbs free energy minimisation | 40 |
| Reactor operating pressure | 1 atm | 29 and 38 |
| Feed ammonia stream conditions | 10 bar, 25 °C | 44 |
| Cooling utility (air/water) | 25 °C | |
The thermodynamic analysis also includes heat balance, which can be evaluated using the following method. Under autothermal conditions, the net heat of oxidation of the steam in the SR (ΔH0SR) plus the heat of combustion of hydrogen should be equal to the heat of oxidation of the equivalent OC in AR (ΔH0AR), defined as below:
![]() | (29) |
In the meantime:
![]() | (30) |
is the fuel fraction of ammonia in the ammonia CLCr process. Fig. 2 shows the energy inputs and outputs in the CLCr process. For the calculation of the heat consumed in FR (Qheat-sink), the following were considered: the heat from input oxides (Qi) and gas (QNH3), the heat remaining in the output reduced oxides (Qo), and direct loss (Qv).
The heat input can be calculated with eqn (31) and (32):
| Qi = miCpi(TAo − 25) | (31) |
| QNH3 = MNH3Cp–NH3(TNH3 − 25) | (32) |
The heat remaining in the output reduced oxides can be calculated with eqn (33):
| Qo = moCpo(TFo − 25) | (33) |
The heat loss in FR vent (Qv) can be collected from the model.
The net heat consumed in FR can be then calculated using eqn (34):
| Qheat-sink = Qi + QNH3 − Qo − Qv | (34) |
For the calculation of the net heat generated in heat source (Qheat-source), the following were considered: the heat from the fuel-fraction of ammonia
, the heat of oxidation of the steam in the SR (ΔH0SR). The heat loss from the AR and SR vent were considered as 0 as the AR gas vent was cooled to 25 °C and the SR gas vent was cooled to be below zero in the model.
The fuel-fraction of the mass flow of ammonia (MNH3-fuel) can be calculated using eqn (35):
![]() | (35) |
The heat of oxidation of the steam in the SR (ΔH0SR) can be collected from the model.
![]() | (36) |
The net heat generated in the SR and AR can then be calculated using (eqn (37)):
![]() | (37) |
000 kg h−1. The Fe2O3 mass fraction was 0.758, with the remainder being the heat carrier, Al2O3. The flow rate of ammonia was fixed at around 1400 kg h−1, simulating the scale of H2 production of approximately 200 kg h−1, capacity suitable for applications in hydrogen refuelling stations or for on-site fuel cells.
As TAo increases, Ered increases due to thermodynamic favourability.45YH2 increases when TAo increases from 880 °C to 890 °C, however, it stablises and decreases when TAo increases further from 960 °C. It can be observed that TFo and TSo increase with TAo, but there is a significant decrease when TAo is around 960 °C. Meanwhile, WFe0.947O suddenly increases from zero when TAo rises above 960 °C, while WFe drops to zero. When TAo is at 960 °C, TFo is about 590 °C, which corresponds to the disproportionation temperature of iron oxide. The phase diagram of iron oxides with the presence of steam shows that the Wustite phase (Fe0.947O) appears when the SR temperature is above the disproportionation temperature.46 Below this temperature, Fe can be directly oxidised to Fe3O4, so the fuel reactor (FR) and the steam reactor (SR) are in the Fe ↔ Fe3O4 phase equilibria. This explains the sudden increase in WFe0.947O as the equilibria shifts from Fe ↔ Fe3O4 to Fe ↔ Fe0.947O ↔ Fe3O4 when TAo exceeds 960 °C.
H2 in the FR vent (VH2) decreases as TAo increases up to 960 °C and then remains almost zero when the TAo is greater than 960 °C, meaning that no hydrogen is produced in the FR. This may be due to the increase in the reduction rate in the FR until the peak value at 590 °C (TFo). In terms of Ered, about 11% (calculation is shown in SI) of Fe2O3 in the FR is unutilised due to the thermodynamic barrier in re-oxidation in the SR.47 In other words, only 89% Fe2O3 contributes to the production of YH2 in the process. When TAo increases from 880 to 960 °C, WFe increases, and more Fe converts to Fe3O4 in the SR. This explains why YH2 remains stable when Ered increases. However, the conversion between Fe0.947O and Fe3O4 in the SR results in a lower YH2 when TAo is above 960 °C.
On the other hand, Ssteam and Sair increase as TAo increases, while XH2 decreases. The increase in Ssteam with TAo is due to the rise in TFo. With a constant total ammonia feed rate (MNH3), the endothermic heat requirement remains unchanged, which causes excess heat carry-over in the reduced iron oxides to the SR. A higher TFo results in a lower steam equilibrium conversion, indicating that more steam is needed to sustain the oxidation of the reduced iron oxides.39 Due to an increased Ssteam, XH2 decreases as TAo rises. The NH3 CLCr process conceptualised in this work consists of an energy-intensive steam production step, which consumes 50–60% of all recovered heat. Additionally, the high steam mass fraction in the SR outlet (1 − XH2) raises the latent heat load, limiting the extent of gas cooling and condensation in the ammonia vaporiser. This results in more compression work in the purification section, due to higher average gas molar mass resulting from higher moisture content in the gas exiting the vaporiser. The step changes can be observed when TAo is around 960 °C for all the three parameters mentioned above. As mentioned previously, the equilibria shift from Fe ↔ Fe3O4 to Fe ↔ Fe0.947O ↔ Fe3O4 leads to significant increases the PH2O/PH2 requirement in the SR, which in turn results in a higher steam consumption and lower XH2. When TAo is lower than 960 °C, Sair increases as more WFe requirement in the AR. When TAo is higher than 960 °C, Sair increases as more Fe0.947O is required to enable a higher reaction temperature in the AR, which compromises the conversion of Fe3O4 to Fe0.947O in the SR.
The results are presented in the form of a mesh plot, showing the flow rate of hydrogen (MH2) at various TFo and steam flow (Fig. 5). The six areas highlighted by the dashed lines represent different states of equilibria inside the SR. Area 6 shows the steam flow rate at different TFo to reach the maximum hydrogen generation (ṁH2, max = 186.9 kg h−1). When MH2 is constant (the horizontal lines shown in Fig. 5), more steam is consumed as TFo increases. The specific steam consumption (Ssteam) increases as steam is consumed faster at higher TFo. Area 1 illustrates the scenario with low Ssteam. At this stage, the system in the SR is in the Fe ↔ Fe3O4 phase equilibria, where lower PH2O/PH2 is required for the conversion.46 This scenario (high MH2 achieved at low TFo) seems advantageous, but Collins-Martinez et al. advised a minimum TFo of 400 °C in the SR to avoid slow kinetics.39 When TFo is higher than the disproportionation temperature (∼590 °C), a stable hydrogen flowrate (80.6 kg h−1) can be observed at low steam flowrate (area 4) (calculation shown in Supplementary Information). As the specific steam flow rate (Ssteam) increases, the hydrogen flow rate increases significantly (area 5). At low Ssteam, the hydrogen is generated from Fe-phase only (area 3). Hydrogen generated solely from the Fe-phase reaches its maximum (80.6 kg.h−1) at area 4. By increasing Ssteam, and there by PH2O/PH2, the equilibria shifts from Fe ↔ Fe3O4 to Fe ↔ Fe0.947O ↔ Fe3O4 (area 5), in which the PH2O/PH2 requirement for Fe0.947O ↔ Fe3O4 is much higher than the previous step (Fe ↔ Fe0.947O). As the temperature increases, the Fe0.947O → Fe3O4 transition become nonspontaneous, meaning higher PH2O/PH2 or higher Ssteam is needed to shift the equilibrium to the right.48 However, area 2 shows inconsistent behaviour in the SR when TFo is between 450 °C and the disproportionation temperature (590 °C). Ssteam slightly increases when TFo drops from 590 °C to 450 °C. Gleeson et al. stated that the Fe0.947O phase was thermodynamically stable beyond 590 °C, and the reduction shifts from Fe ↔ Fe0.947O ↔ Fe3O4 to Fe ↔ Fe3O4 below 590 °C.49 Herein, the exothermic disproportionation reaction (eqn (9)) occurs below 590 °C. The released heat from the reaction (eqn (9)) results in an increase in temperature. At higher Ssteam, less Fe0.947O is available for the disproportionation as Fe0.947O converts to Fe in the SR when MH2 is higher. Thus, TFo has insignificant influences on the hydrogen generation (area 2 shrinks).
![]() | ||
| Fig. 5 Mesh plots of hydrogen production (MH2) as a function of fuel reactor outlet temperature (TFo) and steam flow at TAo = 960 °C, with six highlighted areas. | ||
000 kg h−1 and the ammonia flow rates vary from 1000 to 1900 kg h−1 in order to achieve an ammonia to OC ratio (RNH3/OC) of 10.5–20. The AR outlet is fully oxidised at 960 °C under stoichiometric air flow conditions.
As can be seen from Fig. 6, the flow rate of the feed ammonia has an effect on the overall performance of the process. As RNH3/OC increases, YH2 and Ered in FR increase. TFo and TSo drops continuously as the heat demand in the FR increases. As mentioned previously, Fe0.947O disproportionation occurs when TFo falls to 590 °C. Therefore, XFe3O4 and XFe increase significantly as the phase equilibria shifts from Fe3O4 ↔ Fe0.947O ↔ Fe to Fe3O4 ↔ Fe in the FR, while XFe0.947O significantly decreases. The exothermic reaction (eqn (9)) leads to a sudden rise in TFo. All the hydrogen from ammonia decomposition is consumed until TFo reaches 590 °C. When the disproportionation occurs, VH2 increases with RNH3/OC. The reduction rate of Fe3O4 was found to be maximum at approximately 580 °C, when magnetite was used, and an Ered of 20–60% was applied.50 Herein, the increase of VH2 is due to the drop in reduction rates. This also explains the slower increase in Ered once TFo decreases to 590 °C. The disproportionation in the SR leads to a sudden increase in TSo, which aligns with the observations mentioned previous section, as Ssteam increases below 590 °C. When TAo is at 960 °C and TFo is close to 590 °C, the value of RNH3/OC should be ∼14.5 to achieve the optimal Ered and hydrogen utilisation in the FR.
| Parameter | 1 bar | 5 bar | 10 bar | 15 bar |
|---|---|---|---|---|
| η CGE (%) | 74.19 | 74.13 | 74.03 | 73.95 |
| η OEE (%) | 69.07 | 75.51 | 75.41 | 75.33 |
| Hydrogen purity (%, mol mol−1) | 99.91 | >99.99 | >99.99 | >99.99 |
| WFe0.947O (wt%) | 12.5 | 12.6 | 12.7 | 12.9 |
| ΔTSR (°C kmol−1–O2) | 1.314 | 1.294 | 1.267 | 1.24 |
| W comp (kWh) | 307 | 0 | 0 | 0 |
The cold gas efficiency slightly decreases as the SR pressure increases, with a reduced conversion of Fe0.947O. The temperature rise in the SR decreases, indicating a reduced heat of the reaction. As a result, the mass fraction of Fe0.947O increases with the pressure. The pressure shows a limited impact on the overall performance. Similar trends were reported in previous literature on syngas cracking in CL.52 There is no correlation between pressure and hydrogen purity in the SR vent, which was validated by experiments, as hydrogen purities are beyond 99.99% at higher pressures.
Clearly, the power requirement of the subsequent hydrogen compression can be eliminated when the pressure is above 5 bar, as water condensation is improved by elevating the dew points. This also enhances the latent heat consumption, resulting in an increase in the overall energy efficiency.
A few assumptions were made: (1) the unutilised hydrogen (VH2) for the FR is negligible to maximise hydrogen yield; (2) the FR outlet temperature (TFo) was maintained to be close to 590 °C to exhibit stable phase equilibria; and (3) all reactions in the AR and the SR are stoichiometric.
As shown in Fig. 7, when TAo is around 900 °C and RNH3/OC is 13.60, ηOEE reaches its maximum value (71.7%). When TAo is 880 or 890 °C, YH2 is equal to the theoretical maximum hydrogen yield (YH2, max) but with a sacrifice of ηOEE. At TAo = 900 °C, YH2 starts to drop continuously due to the increase in Ered. In terms of the fraction of fuel energy lost as heat (FL), the system exhibits a lower loss at TAo of 900 °C. Therefore, TAo of 900 °C was selected for the following process intensification.
770.9 MJ h−1 and 19
400.5 MJ h−1, respectively, with an overall exergy efficiency (ηe) of 70.4% (calculated using eqn (26)). Of the total unused exergy, about 71.6% was destroyed during the CLCr process (e.g., high irreversibility of the reactions), and the other 28.4% was wasted in the exhaust streams (spent air and FR vent).53 The exergy destruction mainly arises from the irreversibility of the redox reactions of the Fe-based OC. The extent of irreversibility could be reduced by employing alternative OCs, or combining Fe-based OC with materials with narrower thermodynamic gaps between the reduction and oxidation steps, such as mixed oxides-based materials (e.g., CeO2).54,55 Further exergy reduction could be achieved through enhanced heat recovery or advanced reactor design for better temperature control.
| Streams | Physical exergy | Chemical exergy | Total exergy | |
|---|---|---|---|---|
| Inlet | Ammonia | 392.4 | 24 170 |
24 562.4 |
| Air | −2.7 | 109.3 | 106.6 | |
| Water | 0 | 101.9 | 101.9 | |
| Outlet | Fuel reactor vent | 813.5 | 957.2 | 1770.7 |
| SR vent | 314.2 | 0 | 314.2 | |
| Air reactor vent | −2.1 | 42.7 | 40.6 | |
| Removed water | 0 | −0.4 | −0.4 | |
| Product hydrogen | 0 | 17 275.4 |
17 275.4 |
The levelised cost of hydrogen (LCOH) estimated from the purchased equipment cost was $4.61 kg−1 with the optimised case and the price of the feed ammonia being $0.47 kg−1.56 The price of the feed ammonia was identified to be the largest contributor to the LCOH (84.4%), followed by annual capital expenditure (12.2%), variable operating capital (2.2%), and fixed operating capital (1.1%). The proposed process shows good potential in terms of economic viability, in line with findings from large-scale green ammonia decomposition studies reporting an LCOH of $5.1 kg−1,57 which can be further reduced to $3.4 kg−1 with a cheaper ammonia cost of $0.25 kg−1.
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