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Clean Hydrogen and Ammonia Synthesis in Paraguay from the Itaipu 14 GW Hydroelectric Plant

Massimo Rivarolo
Gustavo Riveros-Godoy
Loredana Magistri
1 and
Aristide F. Massardo
Thermochemical Power Group, DIME, University of Genoa, Via Montallegro 1, 16145 Genoa, Italy
Facultad de Ciencias y Tecnologia, Universidad Privada del Este (UPE), Area 5, Pdte Franco 7700, Paraguay
Author to whom correspondence should be addressed.
ChemEngineering 2019, 3(4), 87;
Submission received: 12 August 2019 / Revised: 16 October 2019 / Accepted: 28 October 2019 / Published: 1 November 2019
(This article belongs to the Special Issue 2019 HYPOTHESIS XIV)


This paper aims at investigating clean hydrogen production from the large size (14 GW) hydroelectric power plant of Itaipu, located on the border between Paraguay and Brazil, the two countries that own and manage the plant. The hydrogen, produced by a water electrolysis process, is converted into ammonia through the well-known Haber-Bosch process. Hydraulic energy is employed to produce H2 and N2, respectively, from a large-scale electrolysis system and an air separation unit. An economic feasibility analysis is performed considering the low electrical energy price in this specific scenario and that Paraguay has strong excess of renewable electrical energy but presents a low penetration of electricity. The proposal is an alternative to increase the use of electricity in the country. Different plant sizes were investigated and, for each of them, ammonia production costs were determined and considered as a term of comparison with traditional ammonia synthesis plants, where H2 is produced from methane steam reforming and then purified. The study was performed employing a software developed by the authors’ research group at the University of Genoa. Finally, an energetic, environmental, and economic comparison with the standard production method from methane is presented.

1. Introduction

Nowadays, fossil fuels still provide more than 80% of the global energy demand [1]. However, since their intensive utilization in the last two centuries, the reserves of fossil fuels (coal, petroleum, and natural gas) are decreasing, especially when considering the continuous growth of world energy demand, in particular in developing countries. Furthermore, fossil fuels have a significant impact in terms of environmental pollution, both at local (emissions of CO, NOx, SOx, and particulate matter) and global levels (due to their extensive CO2 emissions, with the consequent greenhouse effect). To face these energy and environmental problems, the promotion of sustainable solutions [2], including the synthesis of bio-fuels to replace traditional fossil fuels, represents an important step for the future [3,4,5].
Hydrogen has the potential to provide economically feasible, energy efficient, and environmentally sustainable solutions to the above reported issues related to fossil fuels. Hydrogen is a clean energy vector, characterized by zero emissions in terms of both CO2 and local pollutants. Furthermore, hydrogen can be produced throughout the water electrolysis process, employing renewable energy sources (RES) and water as the only input: in this way, the environmental impact in terms of pollutant emissions would be strongly reduced compared to H2 production from steam methane reforming, as reported in [2,6].
Hydrogen production by water electrolysis is a well-known process and several solutions, related to alkaline electrolyzer (AEC) technology, have already been available on the market for the last 50 years. Capital costs have decreased in the last ten years and they are expected to further reduce in the next future: as reported in recent literature [7], different solutions are available in terms of capacity (from kW to multi-MW for unit) and operating pressure (from 1 to 30 bar) with capital costs of about 1000–1200 €/kW for large scale units.
Despite its advantages, hydrogen wide diffusion has yet to face some challenges related to its storage and distribution; in fact, even if hydrogen presents the highest energy content in mass terms, it has, on the other hand, a very low energy density (0.09 kg/m3 at standard conditions) compared to traditionally employed fuels. Figure 1 shows the comparison in terms of gravimetric and volumetric density: it is evident that larger volumes are necessary for H2 storage, due to its low volumetric energy content, leading to higher costs.
For this reason, converting H2 into other fuels or “chemicals”, with higher volumetric energy densities which are easier to store and transport, can be a viable solution, as reported in [9]. The potential advantages of converting renewable hydrogen, produced throughout the water electrolysis process, into methane [6,10] or methanol [11] were investigated by the authors in previous research works. In this paper, the conversion of hydrogen into a liquid carrier, ammonia, is presented.
Ammonia (NH3) has a wide range of applications, in particular in chemical industries, in absorption low-temperature cycles and in agriculture to produce fertilizers: this latest application is of particular interest in the Paraguay context. According to [12] the use of chemical fertilizers in Paraguay has shown an important growth from 2002 to 2014, the annual demand for nitrogenous fertilizers has increased from 34,934 up to 132,558 tons (+379%). NH3 is a gas in standard conditions, but it is relatively easy to liquefy (at −33 °C); therefore, it can be more efficiently stored compared to hydrogen: for this reason, ammonia can be also a convenient energy carrier for hydrogen [13,14]. Since NH3 is liquid at ambient pressure and higher temperatures compared to H2, liquefaction is less energy intensive. Storage and transportation of ammonia is a well-known industrial process: around 150 million of tons of NH3 per year are transported around the world, mainly by ships, rail, and pipelines [15]. Another key advantage of ammonia is that it does not contain carbon or sulphur, therefore it does not contribute to emissions in terms of CO2, CO, and SOx.
Table 1 shows a comparison between hydrogen storage with traditional methods (compressed and liquid hydrogen) and ammonia. Despite its lower power density, ammonia presents a higher energy density; moreover, its storage does not require large amounts of energy input that are required in case of hydrogen, which requires a large energy demand to bring it at high pressures (in case of compressed cylinders, CH2) or at cryogenic temperatures (in case of LH2).
Conventionally, NH3 is produced through the well-known Haber-Bosch process: nitrogen and hydrogen react at high pressure (140–250 bar) and temperature (300–500 °C), in presence of an iron catalyzer [16]. The reaction is exothermic, with the production of 92.4 kJ/mol.
3 H 2   +   N 2     2 NH 3
According to Equation (1), 177 kg of H2 and 823 kg of N2 are theoretically necessary to produce 1 ton of ammonia.
Figure 2 shows the state-of-the-art method for ammonia synthesis in industrial process. H2 is conventionally produced from fossil fuels, through steam reforming of natural gas or coal. Steam reforming is currently the least expensive way to produce hydrogen, and it accounts for most of the commercially produced hydrogen. Due to its advantage from the economic standpoint, this method is widely employed in the industrial field to separate H2 atoms from carbon atoms in methane; on the other hand, the process results in fossil fuel consumption and in significant CO2 emissions. The gas produced by steam reforming has to be purified, separating CO and CO2, before entering the Haber-Bosch reactor for ammonia synthesis, with consequent costs [16,17]. The necessary amount of N2 is separated by air, through an air separation unit (ASU)—despite the process being well-known and the technology mature, a not-negligible amount of energy input is needed in terms of electricity, thermal energy, and fuel consumption. The simplified process is shown in Figure 2.
In this paper, an alternative method for NH3 synthesis is investigated: hydrogen is produced by water electrolyzers, fed only by renewable energy produced from the Itaipu hydroelectric plant (14 GW). The synthesis of ammonia by renewable sources has been studied in recent literature: Tuna et al. [18] performed a techno-economic study of several NH3 production systems based on renewable energy, including electrolysis and biomass gasification; more recently, Bicer et al [19] performed a life cycle assessment of various NH3 generation methods, defining the ecological effects of conventional ammonia generation paths. Producing ammonia from electrolyzers fed by renewable energy sources allows for a significant reduction of the environmental impact as no fossil fuels are consumed and the electrical energy needed in the process is produced by a renewable energy source. Another important advantage is the reduction of plant complexity as purification and gas treatment sections are not necessary anymore in this configuration (no SOx, CO, or CO2): consequently, capital costs and fuel costs decrease.
On the other hand, capital costs related to electrolyzers and electrical energy costs must be taken into proper account. However, it is worth noting that in this particular scenario, electrical energy availability is very large as the hydroelectric plant of Itaipu (14 GW, owned by Brazil and Paraguay) represents the largest renewable facility in the world in terms of energy production. In 2016, the plant obtained the production record of 103.1 TWh, and, in 2017 and 2018, the production exceeded the considerable amount of 96 TWh [20]. In 2018, Itaipu covered 15% of total electrical energy demand of Brazil (9.2 GW in terms of average produced power) and 90% of Paraguay (1.7 GW in terms of average produced power) [20]. It is important to underline that Paraguay owns 50% of the installed capacity in Itaipu (7 GW) but currently uses less than 2 GW. Moreover, Paraguay has another two large size hydroelectric plants, Acaray (220 MW) and Yasyreta (3200 MW), the last one is owned jointly with Argentina.
In periods characterized by large hydraulic availability, water is spilled from the reservoir, without getting to the turbines (20 turbines, 700 MW each) for energy production: in 2017 and 2018, the average spilled power was 214 MW and 81 MW, respectively [20]. This energy, which has a strong time-dependent nature in the different periods of the year, can also be employed for H2 production by water electrolysis. In the other periods of the year, to ensure a constant H2 production, energy could be purchased from the national grid, as investigated by authors in previous works [6,10,11].
The innovative aspect of the present study, compared to the ones reported in recent literature [18,19], is the analysis of a large size plant for ammonia synthesis employing renewable electrical energy only, evaluating the solution not only from the environmental standpoint, but also considering the economic aspects, comparing the average synthesis costs to the standard method.

2. Materials and Methods

In this study, the use of electrical energy from Itaipu for NH3 production was investigated. Hydrogen is produced by large size electrolyzers [21,22] (30 bar, modules of 2 MW, efficiency 75% corresponding to electrical demand of 4.7 kWh/Nm3 H2), while N2 is obtained by an ASU [17] (electrical demand of 160 kWh/ton O2); then, the reactants are compressed and sent to the Haber-Bosch section for ammonia synthesis. Electrical energy for the process is produced by the Itaipu dam. Figure 3 shows a simplified scheme of the plant. Considering that, as reported in the National Energy Balance [23], 73% of the produced electricity is exported (43.6 TWh in 2017), the increase of the internal electrical energy consumption of Paraguay, due to the installation of a large scale power-to-ammonia plant, does not represent a problem for the electric balance of the country. Figure 3 shows a simplified scheme of the plant: it is evident that Paraguay employs only a part of its 50% share, since energy demand is lower than the generated power. Comparing the process with the traditional one, previously shown in Figure 2, it is worth noting that the proposed plant lay-out does not require the sections related to fuel purification (sulphur removal), steam reforming (which include the injection of steam at high temperature) and the CO2 separation from the syngas; thus, the complexity of the plant is significantly reduced.
Assuming a system with a production size of 200 ton/day of NH3, which is a typical commercial scale [16,17], the analysis is performed in two steps: (i) mass and energy flows are calculated to define the size of the main plant components; (ii) the economic analysis is performed, calculating ammonia production costs and performing a comparison with ammonia market values.
The main assumptions considered for the mass and energy flows calculation are reported in Table 2, based on standard values from literature and/or from the industrial market [16,17,21,22].
The resulting mass and energy flows are reported in Figure 3. Considering a nominal production of 200 ton/day of NH3 (equivalent to 8330 kg/h), about 1520 kg/h of H2 and 7100 kg/h of N2 are needed as reactants. H2 is produced by the electrolyzers at 30 bar: with the assumed efficiency, a 2 MW unit is able to produce 38 kg/h; thus, 40 units for a total of 80 MW are needed. As the mass ratio between O2 and H2 in the electrolysis process is 8:1, about 12,160 kg/h of oxygen are co-produced. As far as the N2 is concerned, considering air composition in mass terms (75.6% N2, 23.1% O2), about 2160 kg/h of O2 are co-produced; considering the assumed consumptions for ASU and compressors, an additional 4 MW are required as input.

W-ECoMP Software

As far as the economic analysis is concerned, it is performed throughout W-ECoMP software, developed by the Thermochemical Power Group (TPG) at the University of Genoa [24] and recently employed in several research funded projects [6,11,25,26]. W-ECoMP has a modular structure (more than 50 modules are implemented now), which can be easily combined by the user in order to simulate different kinds of plants (i.e., power to fuel plants, smart grids, combined cycles). One of the most important features of W-ECoMP is the possibility of performing a thermo-economic analysis at two different hierarchical levels to optimize the operating strategy for existing energy systems (low level) and also the size of one or more components during the plant design (high level). Capital and variable costs are considered for the high level optimization, while only variable costs are considered to optimize the operating strategy. In the design optimization, the size of each component is evaluated together with its capital cost. The evaluation of the optimal operating strategy is carried out at the lower level of optimization according to the actual energy load demands (i.e., electricity, heating, and cooling energy). W-ECoMP receives as input: (i) energy load curves versus time; (ii) fuel and/or electricity costs and the economic scenario where the plant operates; (iii) component capital costs vs. size; and (iv) O&M costs vs. time. The software aims at minimizing a cost function (objective function) that is representative of plant annual costs, comprehensive of variable and fixed costs. Fixed costs are evaluated thanks to cost functions, obtained by literature review and/or real market data provided by TPG industrial partners and implemented in the software libraries for each module. The sum of capital costs of the single modules furnishes the purchased equipment cost (PEC). From the PEC, the Total Capital Investment (TCI) can be estimated by considering all the accessory costs (engineering costs, installation costs, land, piping, etc.). The weight of these voices is calculated as a percentage of PEC [11,27] and it depends on the scenario where the plant is operating and on the plant technology. Table 3 shows the main values, assumed in this specific case, based on previous research works [11] and data related to the Paraguayan context: the total TCI/PEC ratio is assumed equal to 1.75. It is worth noting that the values are affected not only by the plant typology, but also by the scenario where the plant is installed.
As far as variable costs are concerned, they include mainly fuel and energy consumptions: in this case, since the considered plant is a power-to-ammonia plant, the main voice is represented by electrical energy cost. Electrical energy cost is based on spilled energy availability in the different periods of the year, according to energy demands from the electrical grid and water availability at the reservoir. Electrical energy costs are assumed to be 7 €/MWh for spilled energy and 30 €/MWh for electrical energy purchased from the grid, when spilled energy is not available or not sufficient to feed the power-to-ammonia plant. More details about the W-ECoMP software have been reported in previous publications by the authors [11,25].

3. Results

In the framework of the present study, different power-to-ammonia system’s sizes were analyzed and compared from the economic standpoint: for each size, NH3 synthesis costs are evaluated and compared with the state-of-the-art process.
As the first step, a fixed size of the system, reported in Figure 3, is considered: purchased equipment costs are calculated considering cost functions implemented in the W-ECoMP software, for the different plant sections, as reported below (compressors costs are included in the Haber-Bosch section):
C e l e c t r o l y s e r s = 1300000 · P m o d 0.9 · N m o d 0.9
C A S U = 204270 · M O x y g e n 0.65
C H a b e r B o s c h = 109000 · M i n 0.65
From the above reported cost functions, the purchased equipment cost (PEC) of the plant is calculated. Adding the accessory costs (reported in Table 2), it is possible to evaluate the total capital investment (TCI) and, therefore, the annual fixed costs. Variable annual costs are mainly related to electrical energy consumption. Figure 4 reports the main results in terms of annual costs and their distribution, considering a fixed plant size for the production of 200 ton/day of NH3 and a capacity factor of 8400 h per year, comparable with the ones available on the market for NH3 synthesis.
Considering the above reported capacity factor of the plant, it is easy to calculate, knowing the annual amount of produced ammonia (70,000 ton/year), the production specific cost, which is 366 €/ton. This cost is lower than the market price of 350–550 $/ton [28] for ammonia synthesis from methane steam reforming (depending on the market price of CH4, which is affected by several parameters). Therefore, the proposed method is economically attractive, at least in the proposed scenario. It is worth noting that the above reported production cost can be further reduced by considering the sale of the high amounts of oxygen co-produced in the electrolysis process and in the ASU, after proper storage and distribution. The O2-selling option is not included in this analysis; however, it would improve economic performance, even if a storage and transportation system would be necessary.
From the environmental point of view, the proposed system presents significant advantages, as it employs only renewable energy, while the traditional system presents high fuel consumption and CO2 emissions. Considering the same plant size in terms of ammonia production (200 ton/day, corresponding to 70,000 ton/year), about 25,000 ton/year of natural gas would be necessary, with a consequent emission of 68,000 ton/year of carbon dioxide. Therefore, the proposed solution also presents a significant advantage in terms of fossil fuels savings and the avoidance of emissions of greenhouse gases (CO2).

Sensitivity Analysis: Effect of Plant Size

The results reported in the previous section refer to a “standard” size of the plant, able to produce 200 ton/day of ammonia, for a total annual production of 70,000 tons. However, the reported value is a standard for a low-medium capacity plant for ammonia synthesis. In this subsection, the economic impact of the plant size is investigated.
Table 4 reports the influence of the plant size in terms of NH3 production costs: the aim of the analysis was to determine the optimal size that allows for annual production costs minimization. Even in this case, the analysis does not take into account the option of oxygen storage, distribution, and selling: the high amount of coproduced O2 is vent into the atmosphere.
It is worth observing that by increasing the power-to-ammonia size, two different phenomena take place:
  • Despite the increase of the overall plant TCI, the specific investment cost becomes lower from the effect of size, from 2875 €/kW for a low-medium capacity plant (200 ton/day of NH3) up to 1888 €/kW for a large capacity one (1500 ton/day of NH3);
  • On the other hand, the amount of low-cost spilled energy available for the ammonia plant gets progressively lower for higher sizes: as consequence, while for lower capacity plants the fixed costs are more significant than variable costs (electrical energy), for higher sizes the situation is the opposite, as electricity has an higher cost (30 €/MWh).
The combination of these two effects is that the optimal value, from the economic point of view, is an intermediate size of about 200 MW: the highest production costs occur at lower sizes (366 €/ton at 80 MW, due to higher capital costs) and at large sizes (383 €/ton at 600 MW, due to higher electricity costs). However, it is worth noting that specific synthesis costs for large size NH3 synthesis from the traditional method (CH4 steam reforming) reported by IEA are in the range 350–550 $/ton [28], meaning that the presented synthesis method is economically feasible. As far as economic analysis is concerned, the results are interesting, thanks to the large availability of low cost electrical energy from the Itaipu plant.
Figure 5 shows the main results, focusing on the trend of annual costs and ammonia specific production cost as function of the plant installed power. It is worth noting how the impact of variable costs becomes more and more significant as the size increases: at the highest size (600 MW), the contribute is about two times higher than fixed annual costs; at intermediate size (300 MW) the two contributes are equal, while at the lowest size (80 MW), fixed costs are significantly higher.

4. Discussion and Conclusions

In this study, a solution for ammonia synthesis from renewable energy has been investigated from the technical and economic points of view, considering as a case study the Itaipu 14 GW hydro power plant, which is the largest hydroelectric facility in the world in terms of energy production, where considerable amounts of low-cost (spilled) energy are available. The hydraulic energy has been employed to produce hydrogen by a large-scale system of commercial pressurized (30 bar) alkaline electrolyzers; then, the hydrogen is mixed with the nitrogen, separated by air with a commercial unit, and the two gases are sent to a chemical reactor for ammonia synthesis. A time-dependent economic analysis has been performed using a software tool developed by the authors, calculating annual plant costs and ammonia synthesis costs. The proposal presents an interesting strategy for greater use of clean electrical energy toward a low carbon economy in Paraguay.
A first energy and economic analysis was performed considering a plant size of 200 ton/day of NH3, then the influence of the plant size was investigated, considering different large size systems in order to optimize the ammonia production cost. The results allowed the following conclusions to be drawn:
  • For all the investigated sizes, ammonia production costs are lower than 400 €/ton, (market prices are 350–550 $/ton), showing a good economic feasibility.
  • For the lowest investigated size (200 ton/day of ammonia, 80 MW of electrolyzers), the plant specific cost is higher (about 2900 €/installed MW) due to the higher specific capital cost of the components.
  • For the highest investigated size (1500 ton/day of ammonia, 600 MW of electrolyzers), capital costs are considerably lower (1900 €/installed MW); on the other hand, since the amount of electrical energy that has to be purchased by the grid is higher, variable costs increase and the production cost increases as well.
  • The best solution is represented by an intermediate size of about 200 MW of installed AECs, as shown in Figure 5, corresponding to a production cost of about 340 €/ton.
  • From the environmental standpoint, the so produced NH3 is 100% green, as it is produced by renewable electricity only; moreover, the emissions of CO2 are avoided, as reported in the previous section.
  • The economic results can be improved by considering the storage, distribution and sale of the very large amounts of pure oxygen produced during the electrolysis process; however, this study would require further analysis related to the O2 market in Paraguay and Brazil in order to evaluate the related transportation costs. This analysis, partially performed by the authors’ research group in a previous study [29], may be integrated in a future work.
In conclusion, the proposed method for ammonia synthesis presents several advantages compared to the state-of-the-art, in particular in environmental terms. Furthermore, considerable amounts of pure oxygen are produced and this could be a significant benefit from the economic standpoint. However, it must be noted that the positive economic results are related to the availability of a very large amount of electrical energy at relative low cost, which depends on the scenario where the plant operates: in countries characterized by large share of renewable electrical energy production, the proposed layout can be a worthy solution.
Finally, it is worth remarking that the proposed approach has a general validity, therefore it can be applied to different plant sizes and different economic scenarios, evaluating the influence of economic parameters (i.e., electrical energy price) on the results.

Author Contributions

Conceptualization, M.R. and A.F.M.; methodology, M.R. and G.R.-G.; software, M.R. and A.F.M.; validation, M.R.; formal analysis, M.R. and G.R.-G.; investigation, M.R. and L.M.; data curation, M.R.; writing—original draft preparation, M.R.; writing—review and editing, A.F.M.; supervision, L.M. and A.F.M.


This research received no external funding.

Conflicts of Interest

The authors declare no conflict of interest.


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Figure 1. Gravimetric and volumetric density of hydrogen and other fuels [8].
Figure 1. Gravimetric and volumetric density of hydrogen and other fuels [8].
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Figure 2. Industrial process for ammonia synthesis from natural gas [16].
Figure 2. Industrial process for ammonia synthesis from natural gas [16].
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Figure 3. Simplified scheme for ammonia synthesis from Itaipu electrical energy.
Figure 3. Simplified scheme for ammonia synthesis from Itaipu electrical energy.
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Figure 4. Total annual costs distribution (left) and detail of fixed and variable costs (right) for a 200 ton/day NH3 plant.
Figure 4. Total annual costs distribution (left) and detail of fixed and variable costs (right) for a 200 ton/day NH3 plant.
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Figure 5. Ammonia specific cost and annual costs (variable and fixed) vs. plant size.
Figure 5. Ammonia specific cost and annual costs (variable and fixed) vs. plant size.
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Table 1. Comparison between hydrogen and ammonia.
Table 1. Comparison between hydrogen and ammonia.
Pressure [bar]700atmosphericatmospheric
Temperature [°C]-−253−33
Density [g/L]3571674
Power density [kWh/kg]33.333.35.2
Energy density [kWh/L]
Energy demand for storageMediumHighLow
Table 2. Main technical assumptions for energy analysis [16,17,21,22].
Table 2. Main technical assumptions for energy analysis [16,17,21,22].
2 MW Electrolyzers
Electrical demand4.7 kWh/Nm3 di H2
Pressure30 bar
O2:H2 mass ratio8:1
Air Separation Unit
Electrical demand160 kWh/ton O2
Haber-Bosch section
H2 compressor efficiency70%
N2 compressor efficiency85%
Working Pressure150 bar
Conversion efficiency96%
H2:N2 mass ratio6:28
Table 3. Main voices for economic analysis in W-ECoMP software.
Table 3. Main voices for economic analysis in W-ECoMP software.
Voice of Cost% of PEC
Instrumentation and control3%
Electrical equipment3%
Civil works10%
Service facilities5%
Direct costs37%
Fixed Capital Investment (FCI)65%
Working capital7%
Table 4. Ammonia synthesis costs for different sizes.
Table 4. Ammonia synthesis costs for different sizes.
Installed Power [MW]80200300400600
H2 (electrolyzers) [kg/h]152038005700760011,400
O2 (electrolyzers) [kg/h]12,16030,40045,60060,60091,200
N2 (ASU) [kg/h]709317,73326,60035,46653,200
O2 (ASU) [kg/h]191247807170943414,340
Total energy demand [GWh]705.71717.52560.73280.35121.4
Spilled energy amount70%65%55%40%25%
Capital costs
Electrolyzers [M€]68.1155.4223.9290.0417.7
ASU [M€]27.750.365.578.9102.8
Haber-Bosch [M€]39.471.493.0112.1145.9
Total PEC [M€]135.2277.2382.3481.6666.4
TCI [M€]236.6485.0669.0841.31166.1
Specific capital cost [M€/MW]29572425223021031943
Annual fixed costs [M€/year]15.732.344.656.177.7
Annual variable costs [M€/year]9.825.844.466.9123.4
Avoided CO2 [103 ton/year]68170255340510
NH3 prod [ton/day]20050075010001500
NH3 prod cost [€/ton]366332343351383

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MDPI and ACS Style

Rivarolo, M.; Riveros-Godoy, G.; Magistri, L.; Massardo, A.F. Clean Hydrogen and Ammonia Synthesis in Paraguay from the Itaipu 14 GW Hydroelectric Plant. ChemEngineering 2019, 3, 87.

AMA Style

Rivarolo M, Riveros-Godoy G, Magistri L, Massardo AF. Clean Hydrogen and Ammonia Synthesis in Paraguay from the Itaipu 14 GW Hydroelectric Plant. ChemEngineering. 2019; 3(4):87.

Chicago/Turabian Style

Rivarolo, Massimo, Gustavo Riveros-Godoy, Loredana Magistri, and Aristide F. Massardo. 2019. "Clean Hydrogen and Ammonia Synthesis in Paraguay from the Itaipu 14 GW Hydroelectric Plant" ChemEngineering 3, no. 4: 87.

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