B.
Coelho
*a,
A. C.
Oliveira
a and
A.
Mendes
b
aNET–New Energy Technologies Research Unit IdMEC–Institute of Mechanical Engineering–FEUP, Faculty of Engineering–University of Porto, Rua Roberto Frias, 4200-465, Porto, Portugal. E-mail: bcoelho@fe.up.pt
bLaboratory for Process, Environmental and Energy Engineering (LEPAE), Faculty of Engineering–University of Porto, Rua Roberto Frias, 4200-465, Porto, Portugal
First published on 23rd June 2010
Today's world suffers from an increasing dependence on fossil fuels, either for electricity production, transportation or reagent for the chemical industry. A technological revolution in hydrogen and electricity production is important to support the future needs and lead the world towards a better future. For that, technological and economical barriers have to be broken. Concentrated solar power (CSP) has been proving to be a valid means to start this revolution and produce electricity and hydrogen from completely renewable sources—water and the sun. Although solid steps should be taken to solve the current limitations and increase the technical and economical viability of these projects, there are conditions to begin this revolution using factual bridges from the current fossil technologies to renewable technologies.
![]() B. Coelho | Bruno Coelho is a mechanical engineering PhD student at the Faculty of Engineering of University of Porto–FEUP. He graduated at FEUP with a masters degree in chemical engineering in 2008 with special emphasis on environment and energy. He has done several presentations at international conferences and is co-author of a few papers under publication. His main research interests are on solar energy and concentrated solar power, especially the production of renewable electricity and chemicals. |
![]() A. C. Oliveira | Professor Armando C. Oliveira is an Aggregate Professor at the Department of Mechanical Engineering of FEUP. He is Head of the New Energy Technologies Research Unit of the Institute of Mechanical Engineering–FEUP. He has coordinated and participated in 13 European research and development projects related to the development of new and sustainable energy systems. He is Secretary General of the World Society of Sustainable Energy Technologies, Executive Editor of the International Journal of Low Carbon Technologies (Oxford University Press, UK) and a member of the Editorial Board of the International Journal of Ambient Energy (Ambient Press Ltd, UK). |
![]() A. Mendes | Professor Adélio Mendes received his PhD degree from the University of Porto in 1993. He is Aggregate Professor at the Department of Chemical Engineering of FEUP. He coordinates a large research team with research interests in a variety of topics, mainly in fuel cells, dye sensitised solar cells, photoelectrochemical cells for hydrogen production, photocatalysis, catalytic membrane reactors, membrane and adsorbent-based gas separations and numerical methods. Prof. Mendes authored and co-authored more than 100 papers and filled 18 patents. |
Broader contextThis review paper looks at the different routes for producing electricity and chemicals from concentrated solar power (CSP). Specifically, the production of hydrogen from water, biomass, fossil fuels, electricity and steam based on CSP power is analysed. This is one of the most up-to-date topics of investigation on energy and environmental science and has a major impact in the research community. In today's fossil fuel dependent world, a technological revolution in fuels and electricity production is important to support the future needs and lead the world towards a better future. For that, technological and economical barriers have to be broken. Concentrated solar power (CSP) has been proven to be a valid means to start this revolution and produce electricity and hydrogen from completely renewable sources—water and the sun. This review addresses the current limitations, technical and economical viability of these technologies, and indicates some possible factual bridges connecting the current fossil technologies to renewable technologies. |
The transport sector is particularly vulnerable to oil supply scarcity, since it is still 95% dependent on oil worldwide.2 It represents 18% of primary energy use and about 17% of global CO2 emissions, with the vast majority of emissions coming from road transport.2 Transport is also responsible for 20% of the projected increase in both the global energy demand and greenhouse gas emissions (GHG) until 2030.3 For example, using solar hydrogen in fuel cell (FC) cars can reduce life cycle GHG emissions by 70%, compared to advanced fossil fuels.4 Solar hydrogen production allows the reduction of fossil energy requirements by a factor of 10 compared to conventional technologies.4 The only environmental impacts are associated with the construction of infrastructures for collecting solar energy, as well as with the hydrogen transport and storage. The major impacts are due to large steel needs for building a CSP plant, since today's steel production technology is responsible for fossil and mineral resource consumption as well as particulate, GHG, and other harmful emissions.4
Regarding these scenarios, hydrogen appears attractive as a fuel because it can solve the major fossil fuel environmental, political and economical down points. Hydrogen is advantageous because it can be produced from water and renewable energy, and can be used in highly efficient fuel cells producing only water as a by-product. This may represent a technological step forward to provide a sustainable energy source that can reduce negative environmental effects on the climate, such as greenhouse gas emissions, and satisfy the world’s future fuel demand.
Large-scale commercial implementation of CSP has been done in California, USA and Spain and is now a successful model for many CSP promoting countries. The bulk of new capacity is seen in the Mediterranean bay, which may lead this region to be the heart of renewable CSP electricity generation. This region has abundant solar radiation, cheap land and high electrical demand. These factors have already propelled the growth of the CSP market in the region, with countries such as Spain, Algeria, Morocco, Israel and UAE investing in the promotion and development of CSP plants.5
The basic operation principle is to concentrate solar radiation into a receiver, specially designed for high absorption and to reduce heat loss. A fluid flowing through the receiver absorbs the heat, and high temperature–high pressure steam is generated to drive a turbine. Air, water, oil and molten salts are used as heat transfer fluids. Electricity can be generated with traditional Rankine power cycles using steam turbines, or with the Brayton cycle using gas turbines, or using Stirling engines. These CSP systems have been proven to be technically and economically viable in large scale megawatt (MW) units focused on the production of electricity on demand. Several authors have described the currently operating and under construction/project CSP plants.6–9 The major plants are based on four different optical configurations: tower, parabolic trough, dish and linear Fresnel.
Parabolic trough collectors (PTC), linear Fresnel systems (LF) and power towers or central receiver systems (CRS) can be coupled to cycles of 10 to 200 MW of electric capacity, with thermal cycle efficiencies of 30 to 40%. On the other hand, Dish-Stirling engines (DSE) are normally used for decentralized generation in the range of 10 kW.4
Within different CSP technologies each has specific and different operating conditions. PTC and LF are 2D concentrating systems able to concentrate the radiation flux 30 to 80 times, heating the thermal fluid up to 393 °C.9 On the other hand, CRS and DSE are 3D concentrating systems that can achieve higher concentration ratios, between 200 and 1000 for CRS and 1000 to 4000 for DSE, with working temperatures above 1000 °C.9
Due to a lower concentration capacity of PTC and LF and the size limitations of DSE, the technology with higher potential for hydrogen production is CRS. With a secondary concentration, CRS systems can achieve concentrations of over 1500 suns and temperatures above 1500 °C. The collected thermal energy can be used to provide heat so that hydrogen is produced by chemical reactions that split the water molecule. Many such reaction sets have theoretical efficiencies around 40%. Combined with annual efficiencies for solar thermal systems of about 45%, the solar-to-hydrogen efficiency of this method could go above 20%, with much lower installed collector costs than photovoltaic systems (PV).10
World CSP implementation is in exponential progress. Currently there are 560 MW of CSP plants in operation, and adding to that, currently there are 984 MW under construction around the world and more than 7463 MW announced to be in development.8 In a moderate technological growth scenario, CSP is expected to achieve above 68000 MW of installed power by 2020 and beyond 230
000 MW by 2030.8
Solar thermochemical applications are not as developed as solar thermal electricity generation, but they employ the same solar concentrating technologies. In order to scale-up solar reactors, parameters such as the reactor volume and the loading with the required redox/catalyst coating have to be optimized, taking into account the solar flux and the resulting temperature distribution, the heat transfer characteristics, the reaction rates and transient phenomena due to reactor operation at alternating solar flux conditions.11
The combination of these systems presents interesting synergies that can be exploited.
Hydrogen transportation and storage is a major logistics problem. Compressed hydrogen storage in lightweight compound bottles or tanks has an energy density of 4.4 MJ L−1 (700 bar) and represents a cost increase of 0.2–1.0 €/kg3 in hydrogen production price. These tanks currently have operating pressures of up to 700 bar. As tank pressure increases, the energy needed for hydrogen compression also increases. To compress hydrogen to 200 bar, 18% of the total energy stored in the tank is spent.12
Depending on the delivery distance, hydrogen liquefaction could also be considered, as the total capital costs could be reduced. For a 100 km delivery distance, the energy consumed percentage to the delivery is 6.27% for compressed hydrogen, while it is 0.87% for liquid hydrogen. These values are still above gasoline (0.19%), propane (0. 27%) and methanol (0.42%).13
Operating pressures for liquid storage of hydrogen range from 1 to 3.5 bar and can provide energy densities of up to 8.4 MJ L−1. The main problems related to liquid hydrogen are the energy required for liquefaction, insulation and boil-off losses. About 30% of the total energy can be consumed in the liquefaction process. Besides, in the current pressure vessels for passenger cars there is a hydrogen loss of 2–3% per day.12 In novel double-walled vacuum insulated tanks these losses could be reduced to 0.2–0.4%.12
Alternatively, hydrogen may be stored in hydride compounds. Metal hydrides could have very good hydrogen densities, up to 151 kg m−3 (aluminium–AlH3), but with a large system mass. Therefore, the gravimetric densities do not exceed 2 wt.% at normal pressure and temperature conditions.13 With auxiliary heating the gravimetric densities can be increased to 7 wt.%.14 Higher densities can be reached with the use of chemical hydrides. Such hydrides are usually formed with elements such as B, Al, Mg, and Li. Compounds such as LiBH4 can reach gravimetric densities of 18 wt.% and Al(BH4)3 can carry 17 wt.% of hydrogen. But compounds that achieve these high efficiencies tend to have slow hydrogen releasing mechanisms. Also, boron hydrides, which provide the highest storage capacities, produce volatile borates, which have high hysteresis and can potentially damage fuel cell systems.12
The vehicle autonomy is another problem to the use of hydrogen as a fuel. Hydrogen storage solutions are not yet able to provide a range greater than 500 km3 while meeting all the performance parameters; also, it is necessary to build a new distribution infrastructure. The costs of transportation and building a distribution infrastructure accounts for 20–40% of total hydrogen costs; the remaining 60–80% share is attributed to hydrogen production.3
Despite the presented difficulty for hydrogen use as a fuel, the hydrogen market for other applications is still a growing market. The hydrogen production technologies can be switched towards sustainability, basing hydrogen production in renewable resources.
There are other CRS technologies currently in the commercialization phase that present interesting electricity costs. That is the case for CRS saturated steam system with an estimated electricity cost of 0.169 €/kW he and the atmospheric air central system with an electricity cost of 0.179 €/kW he.6 One of the most promising systems, though still in the experimental phase, is the pressurized air receiver system which works with a combined cycle, allowing better efficiencies and lower electricity production costs of 0.139 €/kW he.6
These promising prices of electricity can be competitive with other renewable technologies such as photovoltaic (PV). Electrolysis electricity needs could therefore be supported by a CRS plant and hydrogen produced with current commercial electrolysis equipments. Electrolysis could be performed in an acid or alkaline medium. Despite the fact that the discovery of electrolytic water decomposition was first observed in acidic water, in industrial plants the alkaline medium is preferred, because corrosion is more easily controlled and cheaper construction materials can be used. Considering an alkaline electrolyte, hydrogen is generated at the cathode while oxygen is produced at the anode, according to eqn (1) and (2). The charge equalization proceeds by ionic conduction.
2H2O + 2e− → H2 + 2OH− (cathode) | (1) |
2OH− + ½O2 → H2O + 2e− (anode) | (2) |
The major problem of conventional electrolysis is high electricity consumption. It reduces the overall solar-to-H2 efficiency (14%15) and increases the cost of hydrogen (2.1–6.8 €/kg
16) when compared to other approaches. Other technologies for hydrogen production, such as proton exchange membrane electrolysis and steam electrolysis have been developed in more recent years and could get good results, especially with the use of CSP. Steam electrolysis is a technology that can reach higher energy efficiency when compared to alkaline and proton exchange membrane electrolysis. That occurs because a substantial part of the energy needed for the electrolysis process is added as heat, which is much cheaper and efficient than electrical energy. In this system, hydrogen is produced with a solar-to-H2 efficiency of 20%15 and a cost of 5.5–6.7 €/kg.17
The water-splitting thermochemical cycles solve the H2/O2 separation problem and allow operation at relatively moderate upper temperatures. Previous studies performed on H2O-splitting thermochemical cycles were mostly characterized by the use of process heat at temperatures below 925 °C.32 These cycles required multiple steps (one endothermic high temperature step supported by the CSP heat and then followed by exothermic reaction steps) and suffer from inherent inefficiencies associated with heat transfer and product separation at each step. Currently the CSP technology has improved and new, more efficient, cycles have been tested at higher temperatures.
There are, however, as in the direct water thermolysis process, solar peculiarities in comparison to conventional thermochemical processes: high thermal flux density and frequent thermal transitions. Because of the fluctuating solar radiation and weather conditions, variations in the regeneration temperature of the cycles of about ± 50 °C on the receiver have been observed.33 The two most prominent receiver concepts are the volumetric-air receiver and the solid particle receiver.34 Therefore, CRS and thermochemical commercial processes need to be adapted and, to reduce the solar transients, it is ideal to store solar high-temperature heat in a thermal storage system, and use the stored thermal energy continuously. However, thermal storage at temperatures above 450 °C is very difficult to achieve in an economically competitive way.16
From all possibilities, several authors35 compiled a database of 280 thermochemical water cycles. These cycles can be divided into “high-temperature” (Table 1) and “low-temperature” categories (Table 2), based on their number of reaction steps and on the operating temperature, above and below 1400 °C, respectively.
Cycle | Reaction steps | T/°C |
---|---|---|
FeO/Fe3O4 | Fe3O4 → 3FeO + ½O2 | 2000–2300 |
3FeO + H2O → Fe3O4 + H2 | 400 | |
Zn/ZnO | ZnO → Zn + ½O2 | 1600–1800 |
Zn + H2O → ZnO + H2 | 400 | |
Sodium manganese | Mn2O3 → 2MnO + ½O2 | 1400–1600 |
2MnO + 2NaOH → 2NaMnO2 + H2 | 625 | |
2NaMnO2 + H2O → Mn2O3 + 2NaOH | 25 | |
Cadmium carbonate | CdO → Cd + ½O2 | 1450–1500 |
Cd + H2O + CO2 → CdCO3 + H2 | 350 | |
CdCO3 → CdO + H2O | 500 | |
Hybrid cadmium | CdO → Cd + ½O2 | 1450–1500 |
Cd + 2H2O + CO2 → Cd(OH)2 + H2 (electrochemical) | 25 (ambient) | |
Cd(OH)2 → CdO + CO2 | 375 |
Cycle | Reaction steps | T/°C |
---|---|---|
Westinghouse cycle (or hybrid sulfur cycle) | H2SO4 → H2SO4 + H2O | 875 |
H2SO4 → H2O + SO2 + ½O2 | 875–1275 | |
2H2O + SO2 → H2SO4 + H2 (electrolysis) | 80 | |
General Atomics process (or sulfur–iodine process) | H2SO4 →H2SO4 + H2O | 875 |
H2SO4 → H2O + SO2 + ½O2 | 875–1275 | |
2H2O + I2 + SO2 → H2SO4 + 2HI (Bunsen reaction) | 100 | |
2HI → I2 + H2 | 300–500 | |
UT-3 cycle | CaBr2 + H2O → CaO + 2HBr | 700–760 |
CaO + Br2 → CaBr2 + ½O2 | 500–600 | |
Fe3O4 + 8HBr → 3FeBr2 + Br2 + 4H2O | 200–300 | |
3FeBr2 + 4H2O → Fe3O4+ 6HBr2 + H2 | 550–650 | |
Hybrid copper chloride cycle | 2Cu2 + 2HCl → 2CuCl + H2 | 425 |
4CuCl → 2Cu + 2CuCl2 (electrochemical) | 25 (ambient) | |
2CuCl2 + H2O → Cu2OCl2 + 2HCl | 325 | |
Cu2OCl2 → 2CuCl + ½O2 | 550 |
All of the “high temperature” cycles could use CSP heat for thermal reduction of the metal oxide. In the simplest version of the cycle, the oxide is completely reduced to a lower valence state. In the following exothermic reaction, the reduced oxide is put in contact with steam to produce hydrogen and regenerate the original oxide. This is the model for the cycles most closely examined in the literature, Zn/ZnO and FeO/Fe3O4.10 These cycles have only two steps, leading to simple process separations and a low potential for energy losses between cycle steps and during separations. Of all the oxides that are capable of performing the subsequent hydrolysis, ZnO has the lowest decomposition temperature, and would be predicted to have a cycle efficiency of 45% and a solar-to-hydrogen efficiency of 17%.16
The cycle based on the FeO/Fe3O4 pair has also received large amounts of attention in the literature, but its operating temperatures are much higher than in the Zn/ZnO cycle, causing it to lose efficiency and causes material problems. To avoid these problems, some moderated temperature oxide cycles have been proposed: the case of cadmium carbonate (CdO) and sodium manganese (Mn2O3). These oxides, when reduced, do not directly split water, so the process must be achieved through more than one additional step, as shown in Table 1. These steps introduce the possibility of side reactions and the consequent need of complicated separations steps. Sodium manganese exhibits thermal reduction at a lower temperature than ZnO and FeO without recombination problems. However, the subsequent steps of the cycle form a sodium–manganese compound that makes the sodium recovery very difficult.10
Those difficulties are reduced when using a water-splitting cycle, presented in Table 2, which can work at lower temperature. Nonetheless, the cycles with more than three reaction steps suffer from a significant reduction in efficiency, with the use of solar high temperature heat.28 From this perspective, the Westinghouse cycle, with two reaction steps (Table 2), and the General Atomics process with three reaction steps (Table 2), are good solutions. The UT-3 cycle is a clear example of this assessment; the cycle when powered by nuclear energy has an estimated 15% overall efficiency and when operated in solar mode the efficiency is reduced to 8%.36 For the hybrid cycles, an important aspect to determine is the equilibrium of the acid concentration and the cell voltage in order to find the minimum voltage for the best electrochemical efficiency. The hybrid low temperature cycles, which is the case of the hybrid copper chloride cycle, use an electrochemical step to reduce cycle operating temperatures, and can lead to more efficient solar operation and may eliminate some of the complex steps of similar cycles. However, they require the use of electricity that may drive up the final hydrogen cost; on the other hand, these hybrid cycles require less capital.37 Some of the presented water-splitting thermochemical cycles were and are being tested in several projects such as SOLZINC,23 HYDROSOL and HYDROSOL II,24 HYTHEC,38 and STCH.39 The CRS technological experience and knowledge is used to integrate new components and produce a new, high value and high potential product such as hydrogen.
CSP heat can also be used in a great number of different applications other than hydrogen production, such as process heat, handling of hazardous wastes and testing and synthesis of different materials, e.g. carbon nanotubes and refractory oxides.30 In low temperature applications, CSP can be used for seawater desalinization, supplying heat for multi-stage flash evaporation (MSF), multi-effect distillation (MED), thermal vapour compression (TVC) or supplying clean electricity for mechanical vapour compression (MVC) or reverse osmosis (RO) processes.45 CSP can therefore be a means to start solving the alarming water crisis in developing countries with water scarcity, and contribute to the delay of a catastrophic depletion of groundwater resources that would have major effects on economic development and social peace.46 CSP solar heat can also be used to provide solar cooling in separated47 or integrated solutions, with production of power, cooling and water support.48
Cycle | Production costs (€/kg) | Operating temperature of cycle/°C | Cycle efficiencies (%) | Solar to hydrogen efficiencies (%) |
---|---|---|---|---|
a Adjusted prices based on a 50 MW CSP plant.16 b Based on a 46 MW CPC Si-G reactor receiver on a CRS.15 c Based on a solid particle 700 MWth (thermal megawatt) receiver on a CRS.15 d Adjusted prices based on current process designs and small scale pilot plants.17 e Based on a CRS-CSP with day and night operation for a projected output of 20000 N m3 h−1.36 f Hybrid copper chloride cycle with a desalinization plant using nuclear energy and adjusting the capital costs to solar energy.37 g Based on a molten salt 700 MWth (thermal megawatt) receiver on a CRS-CSP plant configuration. The cycle efficiencies consider the efficiency of electricity production by CSP.15 h CRS-CSP with a heliostat field from 2188–8750 m2 with elemental carbon production based on ref. 50. i Based on a 5 kW particle flow reactor in a solar furnace.27 j Based on the SOLASYS reformer with 50 MW power.22 k Based on a 5 kW reactor in a solar furnace.20,21 l Based on ref. 51 and considering a cost increase of 25% for the provision and implementation of the carbon capture costs.16 m Process energy efficiency–energy value of produced hydrogen divided by the energy input—based on ref. 51. | ||||
Metal oxide cycles | 3.5–13a | 1400–2300 | 45–60 b | 17–22 b |
Westinghouse cycle | 3.9–5.6a | 875–1275 | 51c | 22c |
General Atomics process | 2.4–7.9d | 875–1275 | 45c | 19c |
UT-3 cycle | 3.9–4.2e | 700–760 | 47e | 8e |
Hybrid copper chloride | 4.0–5.5f | 550 | 49g | 23g |
Water electrolysis with CSP electricity | 2.1–6.8a | — | 30g | 14g |
High temperature solar steam electrolysisa | 5.5–6.7d | 750–950 | 45g | 20g |
Solar methane cracking | 3.0–3.9h | 1600–1900 | 70h | 9.1–31i |
Solar steam reforming of methane | 1.8–1.9j | 900 | 86j | 63j |
Solar petroleum coke gasification | — | 1600–2100 | 48–87k | 9–20k |
Commercial coal gasification (with/without carbon sequestration) | 0.8/0.64l | 600–1000 | 63m | — |
Commercial natural gas steam reforming (with/without carbon sequestration) | 0.66/0.53l | 900 | 83m | — |
Biomass gasification | 0.85–1.7l | 1100 | 40–50m | — |
Photocatalytic water splitting | 3.5l | — | 10–14m | — |
Hydrogen produced by the General Atomics process has the lowest production cost when compared to Westinghouse, UT-3 and hybrid copper chloride cycles. The hydrogen produced from the metal oxide based cycle has the greatest variation in production costs and is well above all low temperature cycles in the worst price scenario (Table 3). These high costs are mainly due to the high consumption of metal oxide that is not currently produced on a large scale. The production cost differences among all the water thermochemical cycles are not very expressive and, due to the early stage of market implementation, it is still undefined what cycle would be the cheapest one. In terms of thermochemical cycle efficiency, metal oxide cycles can achieve the highest efficiencies. Depending on the metal selected, the cycle efficiencies vary from 45 to 60%. Afterwards, depending on the receiver configuration, the optical and receiver efficiencies vary from 50 to 55% and 67 to 78%, respectively, and determine the solar-to-hydrogen efficiency of 17 to 22%.
Comparing renewable technologies with the current methods, there are significant differences in hydrogen production costs. Today's hydrogen is mainly produced from steam reforming of natural gas without carbon sequestration, which has significantly lower costs than hydrogen generated from water. However, the currently produced hydrogen from natural gas releases 7.3 kg of carbon dioxide per kilogram of hydrogen; if the hydrogen production is from coal gasification, the emissions would increase to 29 kg CO2/kg H2.49 Even if carbon sequestration is considered, the prices of hydrogen production would still be unmatchable to the remaining technologies.
Solar steam reforming of methane can be a first step for the integration of CSP in hydrogen production. It presents a lower hydrogen price than methane solar cracking and is the method with lower hydrogen equivalent cost after current hydrogen production technologies. This method could be the earlier described technological bridge from current technologies to completely renewable hydrogen production from water. The early stage petroleum coke gasification method, based in CSP could be another interesting method. It uses an unexplored and rich fraction of the refineries products to produce a valued product such as hydrogen, with interesting efficiencies.
Another technology that should be considered is biomass gasification. Although there are still some major difficulties in cleaning the syngas, the best case hydrogen price scenario could be competitive, as presented in Table 3.
Electricity generated from CSP can also be used to perform water electrolysis. This system could function as a module of the CSP power plant, conferring flexibility and a means to easily convert electricity excesses into a market added-value product. Electrolysis presents, nevertheless, lower overall efficiencies when compared to water thermochemical cycles. This is due to significant larger losses in the electricity generation power block. However, the high temperature solar steam electrolysis is expected to achieve solar-to-hydrogen efficiencies of about 20% and could therefore be considered a competitive solution.
Large scale production of hydrogen from water could be a long-term solution after the possible implantation of hydrogen as a fuel. Water direct thermolysis and thermochemical cycles have been extensively studied and tested and could be future processes for renewable hydrogen production. Nevertheless, there is still a need for some breakthroughs that can solve the current technological problems. However, the costs and efficiency estimates are promising for water thermochemical cycles such as metal oxide, sulfur iodine and hybrid sulfur cycles. Hydrogen produced from electrolysis could also be a viable renewable solution to hydrogen production if based on CSP electricity, but would have predicted efficiencies below water thermochemical cycles. To boost efficiencies, high temperature steam electrolysis may be used but the current associated costs are slightly above the best cost scenario for other technologies.
Meanwhile, biomass gasification and concentrated solar power cracking/reforming/gasification of fossil fuels with carbon sequestration, particularly methane solar steam reforming, present themselves as bridges that can provide several competitive solutions to assure the current hydrogen demand of the world is met and encourage the use of hydrogen as a fuel, shifting the economy from fossil to renewable energy.
Footnote |
† This article results from the Hyceltec 2009 meeting. |
This journal is © The Royal Society of Chemistry 2010 |