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sustainability Article Novel Use of Green Hydrogen Fuel Cell-Based Combined Heat and Power Systems to Reduce Primary Energy Intake and Greenhouse Emissions in the Building Sector Jordi Renau 1,*, Víctor García1, Luis Domenech 1, Pedro Verdejo 1, Antonio Real 1, Alberto Giménez 1, Fernando Sánchez 1, Antonio Lozano 2and Félix Barreras 2 Citation: Renau, J.; García, V.; Domenech, L.; Verdejo, P.; Real, A.; Giménez, A.; Sánchez, F.; Lozano, A.; Barreras, F. Novel Use of Green Hydrogen Fuel Cell-Based Combined Heat and Power Systems to Reduce Primary Energy Intake and Greenhouse Emissions in the Building Sector. Sustainability 2021, 13, 1776. https://doi.org/10.3390/ su13041776 Academic Editor: András Reith Received: 30 December 2020 Accepted: 2 February 2021 Published: 7 February 2021 Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations. Copyright: © 2021 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https:// creativecommons.org/licenses/by/ 4.0/). 1Technical School of Design, Architecture and Engineering (ESET), Cardenal Herrera CEU University (UCHCEU)—CEU Universities, C/San Bartolomé55, 46115 Alfara del Patriarca, Valencia, Spain; [email protected] (V.G.); [email protected] (L.D.); [email protected] (P.V.); [email protected] (A.R.); [email protected] (A.G.); [email protected] (F.S.) 2LIFTEC, CSIC-University of Zaragoza, C/María de Luna 10, 50018 Zaragoza, Spain; [email protected] (A.L.); [email protected] (F.B.) *Correspondence: jordi.r[email protected] Abstract: Achieving European climate neutrality by 2050 requires further efforts not only from the industry and society, but also from policymakers. The use of high-efficiency cogeneration facilities will help to reduce both primary energy consumption and CO 2 emissions because of the increase in overall efficiency. Fuel cell-based cogeneration technologies are relevant solutions to these points for smalland microscale units. In this research, an innovative and new fuel cell-based cogeneration plant is studied, and its performance is compared with other cogeneration technologies to evaluate the potential reduction degree in energy consumption and CO 2 emissions. Four energy consumption profile datasets have been generated from real consumption data of different dwellings located in the Mediterranean coast of Spain to perform numerical simulations in different energy scenarios according to the fuel used in the cogeneration. Results show that the fuel cell-based cogeneration systems reduce primary energy consumption and CO 2 emissions in buildings, to a degree that depends on the heat-to-power ratio of the consumer. Primary energy consumption varies from 40% to 90% of the original primary energy consumption, when hydrogen is produced from natural gas reforming process, and from 5% to 40% of the original primary energy consumption if the cogeneration is fueled with hydrogen obtained from renewable energy sources. Similar reduction degrees are achieved in CO2emissions. Keywords: hydrogen; PEM fuel cells; cogeneration; building sustainability; energy saving 1. Introduction Europe aims to achieve climate neutrality by 2050, which means net-zero greenhouse gas emissions. Entire society and economic sectors must join this task to reach the final objective, from industry to mobility, building, agriculture, etc. Building sector in Europe consumed 40% of the final energy in 2018, with just household being 26% of the final energy, similar to the industry sector [ 1 ]. According to the Spanish “Instituto para la Diversificación y Ahorro de la Energía (IDAE)” report [ 2 ], space heating and sanitary hot water are responsible of 58% to 75% of the final energy consumption in flats and singlefamily houses in Spain, respectively. Single-family houses account for the biggest energy share supplied from renewable energy, which is close to 40% in the Mediterranean area. However, this is not enough to meet the 2050 EU objective, because 47% of the energy supply still comes from fossil fuels. The Energy Performance of Buildings Directive (EPBD) (2010/31/EU) [ 3 ] is the legislative framework “to achieve a high energy efficiency and decarbonize building stock by 2050”. EPBD states that from 31 December 2020 all new edifications must be nearly zero-energy buildings (nZEB). These are “buildings with a Sustainability 2021,13, 1776. https://doi.org/10.3390/su13041776 https://www.mdpi.com/journal/sustainability
Sustainability 2021,13, 1776 2of19 very high energy performance and the low amount of energy that these buildings require comes mostly from renewable sources”. Primary energy consumption analysis is how the EPBD evaluates the building energy efficiency due to the variety of energy sources that are used. “The concept of primary energy attempts to provide a simple metric for all forms of energy that are supplied to, transmitted through, a defined boundary” [ 4 ]. The EPBD leaves the member states to determine the methodology to calculate the primary energy factor and CO 2 emissions for each end-use energy source depending on the energy supply grid circumstances. Improving energy efficiency and the share of renewable sources are also main targets of the Spanish Government, as they are reflected in the Integrated National Energy and Climate Plan 2021–2030 [ 5 ]. According to this plan, high-efficiency renewable cogeneration facilities are going to be part of the comprehensive strategy for energy efficiency in cities. 2. Background Cogeneration, also known as combined heat and power system (CHP), shows the ability to decrease primary energy consumption and reduce greenhouse gas emissions due to the increase in building energy efficiency [ 6 , 7 ]. Thermal energy demand can be supplied by a heater or a boiler, but the use of the CHP technology could provide the same thermal energy consumption and a fraction or the whole electrical demand depending on the CHP technology used. CHP technologies must be easily scalable for low power ratios to make them suitable for residential applications. CHP systems for buildings can be classified depending on the rated thermal power as micro- (1–5 kW) and small-scale ( ≤ 50 kW) units [ 8 ]. Because CHP systems produce the energy at the point of use, they can be referred as decentralized energy sources [ 9 ]. This advantage of decentralized generation includes an improved energy efficiency, which means an optimized fuel utilization that results in decreased CO 2 emissions and primary energy consumption and a reduction in the national transmission losses, that account for 2%–11% of the losses in the European transmission network [ 10 ]. However, benefits of the distributed generation are only achievable if there is a proper energy management between generation and consumption [ 10 ]. Proper management would require of an energy storage system. Electrical energy storage (EES) improves the self-consumption ratio for small CHP units [ 11 ] and thermal energy storage (TES) eliminates system oversize and also optimizes the use of produced energy [ 12 ]. All the CHP units considered in this paper will integrate both EES and TES systems. Figure 1shows the different CHP technologies suitable to be installed in a residential building [ 13 ]. The zones have been delimited using the technical parameters obtained from the “Cogen Challenge Project” document [ 14 ], where micro-scale and small-scale cogeneration technologies are analyzed. Each technology is represented as a colored fuzzy area, delimited by four straight lines, two thick solid lines and two dotted ones. Thermal/electrical efficiency is indicated in the vertical axis and thermal/electrical rated power in the horizontal one. The represented surface covers the power range for the applicability in buildings, from single-family houses to blocks of apartments. The figure can be read as follows. Solid lines represent two possible CHP configurations in each technology. The right-side solid line of each area indicates the most common or typical “small-scale” unit of the technology and the left-side one corresponds to the smallest CHP unit possible as indicated in [ 14 ]. Solid lines can be understood as an operating point of the real CHP unit, where the upper extreme of the line is for the CHP unit thermal characteristic and the lower one corresponds to the electrical one.
Sustainability 2021,13, 1776 3of19 Figure 1. Comparison of the technical parameters in different gas-fueled combined heat and power technologies. For example, the solid line of the right side in the blue area means the “typical smallscale gas turbine CHP unit” as stated in [ 14 ], which means a rated electrical power of 250 kW and around 330 kW for its rated thermal power. The corresponding conversion efficiencies, around 30% and 40% for the electrical and thermal energies respectively, are read in the vertical axis. On the left side of the same fuzzy area, the electrical and thermal rated power of the smallest gas turbine CHP unit analyzed are 30 kW (26%) and 50 kW (47%), respectively. Both units are connected with the dotted lines that create the fuzzy area, which can be considered as an operational chart for the technology in the small-scale use. In other words, this area can be understood as the operating range for each technology. According to Figure 1the following conclusions can be extracted: • Stirling CHP technology is suitable for any kind of fuel. Its performance is similar to that of a boiler due to its high thermal energy conversion efficiency with the additional benefit of the electrical production that can compensate some of the building intakes. Nevertheless, the heat-to-power (HtP) ratio, which is an important selection parameter [ 15 ], is too high for residential uses meaning that the energy production is unbalanced with respect to the thermal energy demand. Stirling technology is included in Figure 1chart due to its scientific interest, but it is not going to be considered in the present analysis. • Gas turbine and internal combustion engine (Gas ICE) are mature technologies that can be scaled from small to large sizes. Both can consume natural gas, which is a fuel widely available in the residential building sector, but its consumption should be minimized due to environmental constraints. The use of pure hydrogen into ICEs and turbines has several technical problems that is now under research and still need to be improved [16]. In this paper both options are going to be analyzed. • Fuel cell-based CHP (FC-CHP) is the most promising technology due to its balanced heat-to-power ratio, better adapted to the residential building energy profiles, which are more electricity demanding [ 17 ]. Fuel cell presents the highest electrical conversion efficiency. Fuel cells are easily scaled from few watts or kilowatts to hundreds of
Sustainability 2021,13, 1776 4of19 kilowatts keeping a constant energy conversion efficiency when they are fueled from pure hydrogen [ 18 – 21 ]. When this pure hydrogen comes from a green production process, the energy obtained can also be considered as green or carbon-free. FC-CHP are classified as a function of the fuel cell technology used in the power unit. The most common technologies in commercial units are based on polymer exchange membrane fuel cells (PEMFC), The most successful examples of these systems can be found in Japan and Europe [ 22 , 23 ]. PEMFC can be classified into low- (up to 80 ◦ C) and hightemperature (from 120 ◦ C to 180 ◦ C) devices. They only differ in the working temperature required by the polymer used as solid electrolyte membrane. Low-temperature PEM fuel cell-based CHP systems are the most common. In this paper both PEM technologies are considered, paying special attention to a high-temperature PEM fuel cell-based microCHP system specifically conceived in the framework of the MICAPEM project that is been integrated into an existent nearly-zero energy house, developed and built for the international Solar Decathlon 2012 contest [ 24 , 25 ]. The use of high-temperature PEMFC is promising due to the improved chemical kinetics in the electrodes, better tolerance to CO impurities in the fuel, simplification of the water management because it is produced in vapor phase and simpler and compact heat recovery system because of the higher enthalpy of the thermal energy [ 26 , 27 ]. A majority of the significant studies in the literature involving a high-temperature PEM fuel cell-based CHP system are theoretical works [ 28 – 31 ] Only one report on tests in an experimental facility has been found [32]. The objective of this research paper is to expose, using numerical simulations, how fuel cell-based CHP systems can drive a potential reduction of primary energy consumption and CO 2 emissions in the building sector. Numerical simulations are performed using preliminary results from the characterization of the high-temperature PEM fuel cell prototype built and tested to be installed in a demonstrative scale CHP facility. Once installed, the CHP technology will be evaluated and a novel oil-based refrigeration system for HTPEMFC will also be tested, as explained in Section 3.3. In the same project framework, a hydrogen electrolyzer integrated with the solar system is also being installed to link with the green hydrogen source requirement objective. 3. Methods and Materials Numerical simulations were performed using the electrical and gas energy consumptions from four real dwellings in the east coast (Mediterranean area) of Spain. Weather in this region can be classified as a “Csa climate” with hot, dry summers and cool, wet winters, according to Köppen climate international classification [33]. Using the information from actual energy invoices, four daily consumption datasets have been created. Four 10-apartment building consumption profiles were determined considering simultaneously factors from the single dwelling datasets. The selected dwellings are described as follows: • Id 1: 140 m 2 two-story terraced house, four inhabitants. The gas consumers are the boiler, used for heating and on-demand sanitary hot water, and the kitchen cooktop. • Id 2: 75 m 2 flat, four inhabitants. Natural gas is consumed only in the on-demand water heater. Electrical induction cooktop. • Id 3: 90 m 2 flat, four inhabitants. Gas-powered boiler for heating and hot water production. Electrical induction cooktop. • Id 4: 90 m 2 flat, three inhabitants. Natural gas-powered on-demand water heater. Electrical cooktop and individual electrical oil heaters in each bedroom. Data obtained from the gas and electrical utility invoices are one-month aggregated information that must be statistically treated to create the useful datasets to simulate the daily energy demand of the users. The numerical treatment has consisted of normal randomized daily energy consumption estimation using the daily seasonal average consumption values and its seasonal data standard deviation (Figure 2). This process was applied to both energy invoices (electricity and gas), taking the billing date into account to correct the consumption data of the different energy suppliers.
Sustainability 2021,13, 1776 5of19 Monthly invoice Consumption per day Year dataset. Monthly aggregated Seasonal average consumption and deviation Statistical Randomization Dataset Figure 2. Statistical analysis from the annual energy invoices to randomize a daily energy consumption dataset for each building using seasonal values (average and standard deviation). The results of the treatment of the numerical data can be observed in Figure 3, where the vertical axis is the daily electrical consumption and the horizontal one represents the daily thermal energy one. Darker dots are the daily consumption calculated from the utility invoices and the “x” markers are the randomized values obtained from the numerical treatment. Figure 3. Result of the numerical treatment of the utility invoices to create an energy consumption dataset for each dwelling.
Sustainability 2021,13, 1776 6of19 Electrical and thermal data in Figure 3are correlated values, where two main tendencies can be observed. Dwellings with gas-powered heating facilities (Id 1 and Id 3) show a greater thermal energy demand for heating seasons. This results in two different “x-clouds”: one energy demand cloud at the right-top side of the chart (Id 1: from 30 to 50 kWh th. , Id 3: from 15 to 30kWh th. ), where the heating demand can be detected; and a second cloud below 15 kWh th. that is overlapped with the two less-thermal demanding dwellings (Id 2 and Id 4). In the case of dwellings Id 2 and Id 4, the seasonal variation is notorious in the vertical axis due to the increase in the electrical energy demand during the heating season caused by the use of electrical heaters. When the thermal demand is limited to hot water, the energy consumption is function of the number of inhabitants as can be observed for the daily energy thermal values for Id 2 and Id 4, respectively. Heat-to-power (HtP) is calculated as the thermal demand over the electrical demand. This ratio is a season-dependent value, and normally a year-based calculation is provided. The results obtained with the datasets sorted in decreasing order are 3.4 (Id 1), 2.3 (Id 3), 1.5 (Id 2) and 0.7 (Id 4). Considering each dwelling dataset, four 10-dwelling buildings were created using a randomized factor to simulate a centralized CHP. Heat-to-power ratios for the building datasets are similar in value and order. 3.1. Simulation Algorithm Cogeneration facilities are designed to supply the user’s thermal energy demand and to provide electricity as a secondary energy source [ 15 ]. Industrial-scale CHPs use the heat directly, but residential-scale CHPs require a thermal energy storage system (TES) to manage the energy demand avoiding system oversizing [ 12 , 34 ]. Because of this, two simplifications have been assumed for the simulation analysis. The first simplification is that thermal energy demand is supplied daily from a thermal energy buffer (Figure 4) , that can be charged with the CHP unit and discharged by the user without any time dependence. The second simplification is that the electrical energy is also managed using an electrical energy storage system (EES) with the suitable capacity to manage the daily consumption. EES ensures the generation–consumption correlation [ 24 ]. Electrical energy surplus is daily exported to the electrical grid. CHP CHP Fuel Thermal demand Electrical demand Thermal buffer Electrical buffer Electrical Grid Back up heaterGas Figure 4. Cogeneration functioning block diagram for the simulation algorithm. Figure 4shows the functioning block diagram of the CHP system for the simulation algorithm programmed in a Python [ 35 ] script that is graphically described in Figure 5. The code is used to evaluate a day-by-day energy balance from the user dataset for each individual dwelling and the 10-dwelling buildings.
Sustainability 2021,13, 1776 7of19 Thermal demand ( ) Electrical demand ( ) CHP thermal rated power ( & ) Estimated daily operation time () Thermal performance ( ) ≥ 24 hours < 24 hours %& $$ ! % # %& $$ ! % ! % % ! $ $ % # > 0 ≤ 0 " % % " % % Figure 5. Python script code algorithm for day-to-day energy analysis decision diagram. The calculation process starts with the evaluation of the total time that the CHP requires to produce the daily thermal demand, which will depend on the rated thermal power of the CHP technology used. This time can be calculated with the equation: t=QD . QCHP·ηQ , (1) where QD is the daily thermal energy demand, . QCHP is the rated CHP thermal power and ηQ the thermal efficiency of the energy conversions required to feed the demand. Energy
Sustainability 2021,13, 1776 8of19 conversions are due to the energy extraction process of the thermal energy from the buffer used to match the energy production and demand (Figure 4). The same efficiency (85%) is considered for all the CHP technologies. The result of Equation (1) is the time that the CHP requires to produce the daily thermal energy, where two different situations can occur. If the total time calculated is lower than 24 h, the CHP technology is capable to provide the entire daily thermal demand and no back-up energy system will be required. In case of a CHP technology that is not suitably sized the total estimated time can be greater than 24 h, and the maximum achievable energy will be the obtained from the CHP unit working at the rated power the entire day. In this case, it is considered that the shortage of thermal energy will be compensated by a back-up system, e.g., a boiler, using natural gas as fuel. The fuel consumption to produce the thermal energy with the CHP can be determined as: Qfuel =QCHP ηQ CHP , (2) where QCHP stands for the thermal energy produced by the CHP unit, and ηQ CHP is the energy performance for the thermal energy flow in the CHP system. The back-up energy ( Qbackup ) equals the lack of thermal energy because the value comes from the boiler consumption as can be read in Figure 5. The electrical energy produced with the CHP unit depends on the CHP gas consumption and the electrical efficiency of the unit, ηW CHP, as: WCHP =Qfuel·ηW CHP·ηW, (3) where ηW is additional electrical efficiency due to the energy conversions. The electrical energy produced will be used to provide the daily electrical energy demand ( WD ). The electrical energy balance is determined as: Wbal =WCHP −WD. (4) Attending to the sign value reported from this equation, electrical energy will be imported from the grid when it is negative and exported or sold to the grid if it is positive. 3.2. Primary Energy Factors Primary energy (PE) is a concept used to compare different kinds of energy sources, but the scale used in the calculations is relevant [ 4 , 36 ]. In this research, the primary energy factors published by the Spanish Government in 2016 [ 37 ] are used to determine the building performance required for legalization. Corresponding values are summarized in Table 1for both utilities considered, namely, the national electrical grid and the natural gas supply facility. The PE factor depends on the energy carrier and relates the primary energy consumed to provide one kWh to the end-user, in this case the final energy consumed by the residential users. PE factors are also divided into renewable and non-renewable. As can be observed in Table 1, renewable factors are smaller that non-renewable ones, but they are values above zero. This means that a certain amount of energy is required to serve the renewable source, i.e., maintenance tasks. Table 1. Primary energy factors and CO 2 conversion factor established by the Spanish Government for the electrical and natural gas utilities. Primary Energy kWhprimary/kWhfinal No Renewable Source Primary Energy kWhprimary/kWhfinal Renewable Source CO2Emission Factor kg CO2/kWhfinal National electrical utility 1.954 0.414 0.331 Natural gas utility 1.190 0.005 0.252
Sustainability 2021,13, 1776 9of19 Not only the PE, but also the CO 2 emissions will be compared to determine the benefits of the cogeneration technologies. The PE reductions are measured from the initial situation, and they can be evaluated using the equation: PE =QD·fPE g+WD·fPE e, (5) where fPE stands for the primary energy factor (subscripts g and e represent gas and electricity, respectively), QD is the total thermal energy demanded and WD stands for the total electrical energy. The PE consumption with the use of a CHP system will depend on the technology. A general case is shown in Equation (6): PECHP =Qfuel +Qbackup·fPE g+WImp·fPE e−WExp·fPE e, (6) where exported energy ( WExp ) is considered as a primary energy decrement due to its decreasing effect in primary energy consumption. When hydrogen or any other fuel obtained from renewable energy sources is used, the gas terms ( Qfuel and Qbackup )in Equation (6) can be neglected. Carbon emissions can be calculated using the same equations, just replacing the primary energy factors with the CO2emission factor (fCO2). CO2=QD·fCO2 g+WD·fCO2 eand (7) COCHP 2=Qfuel +Qbackup·fCO2 g+WImp·fCO2 e−WExp·fCO2 e. (8) 3.3. Fuel Cell Stack and Its Cooling System Design The power unit of the CHP in the present research consists of a prototype of hightemperature PEM fuel cell and its novel cooling system that were designed and developed specifically for this project. The 40-cells high-temperature PEM fuel cell stack (HT-PEMFC) is formed by 41 JP-945 graphite bipolar plates 280 mm high × 195 mm wide × 5mm thick manufactured by Mersen, as well as two stainless steel end plates where all the connectors for the reactant gases, H 2 and O 2 /air, are placed. The flowfield geometry in both anode and cathode sides consisted of straight parallel channels with a land-to-channel ratio of 1, as recommended by the MEA manufacturer. The anode side was formed by 47 channels 1 mm wide, 1.5 mm deep, and a total length of 210 mm, while the cathode side is formed by 87 channels with a width of 1 mm and a depth of 2 mm, and a total length of 120 mm. With this design, pressure losses were minimized to 5.87 Pa in the anode and 2.6 Pa in the cathode, ensuring both the homogenous distribution of the reactant gases over the electrodes and the correct water management. Commercial high-temperature membrane-electrode assemblies (MEAs) G1018 Dapozol-110, manufactured by Danish Power System (DPS) with a rectangular active area of 163.5 cm 2 , were used [ 38 ]. The MEAs are formed by phosphoric acid doped PBI polymeric membranes, with a nominal thickness of 6 50 ±50 μm , gas diffusion layers of non-woven carbon paper and a platinum load of 1.5 mg cm −2 in both electrodes. The nominal thickness of the electrodes is 250 μ m, including the GDL, the microporous layer and the catalyst layer. To obtain the best results, a minimum compression rate of 13% is advised, as well as a recommended working temperature ranging from 150 ◦ Cto180 ◦ C. Figure 6a shows the manufactured prototype developed by the PEMFC research team from LIFTEC-CSIC in Zaragoza (Spain), which has an ample expertise in this field [ 39 , 40 ]. Figure 6b shows the electrical and thermal performance of the HT-PEMFC stack. The vertical axes represent the voltage (left axis and red curve) and the power (right axis and green curves), and the horizontal values are the current produced by the electrochemical device. Solid green line corresponds to the electrical power, and the dashed green line is the estimated thermal power.
Sustainability 2021,13, 1776 16 of 19 thermal CHP units (“gas ICE” and “gas turbine”) result in a worst PE reduction for all dwellings due to the low operating time (see Figure 12a) and, consequently, the lowest electrical energy production (see Figure 9a). The negative value in the PE ratio for fuelcell-based CHP units is due to the electrical energy surplus. Figure 7a1 shows, again, an optimal design point in the “MICAPEM rated ” characteristics. For the 10-dwelling buildings, the higher the power the higher the PE reduction due to the ability to provide the energy demands from a low consumption of carbon-free fuel for PE production. The contrary can be observed in Figure 7a2 for the “natural gas scenario”, where a greater fuel consumption is penalized. Figure 8a1,a2 show the CO 2 reduction results for the “gas-fueled scenario” for both individual and building dwellings, respectively. The use of CHP in dwellings does not have a carbon emissions reduction due to the higher gas consumption because of the efficiency reduction compared to the use of a boiler. Nevertheless, the 10-dwelling building simulation shows that CO 2 emissions are lower for the fuel cell-based system due to the electrical generation and the increase in global efficiency. Similarly, in both the “green fuel scenario” and the “expected scenario”, the reduction of CO 2 emission shows the same behavior compared to the PE reduction. The size of the CHP system is an important design and a critical economical parameter. The size of the CHP is directly related to the ability to meet the energy demand, but indirectly related to the operation time (and the economic viability). Figure 11 shows the share of thermal energy demand produced with the CHP system and Figure 12 the share of operation hours per year. The total operating time for the smaller units of the “gas ICE” and the “gas turbine” CHP units applied to low thermal demand consumers like a single dwelling (Figure 12a), makes its use unviable (less than 5%-year hours). “Gas turbine” units still are unviable for typical buildings in Spain (less than 20%-year hours). Contrary, fuel cell-based technologies, due to their lower power appear to be a better solution for CHP systems in the building sector, ca. 80%-year hours in the best cases. The low thermal power is not a handicap because fuel-cell-based CHP systems are fully scalable. 6. Conclusions When the primary energy (PE) consumption in Spanish buildings is calculated with the official factors summarized in Table 1, which depend on the energy carrier and its energy source, it was demonstrated that the electrical energy carrier is 1.6 times more demanding than the natural gas from non-renewable sources. Even so, there is a tendency to electrify the consumptions because it is an energy carrier that can be more easily decarbonized. Some industrial heating systems are electrified due to the availability of powerful transmission lines. Despite of this, building centralized heating systems are not normally electrified because of the limitations of electrical grids in the cities. Fuel cell-based CHP systems are a good solution to provide the energy demand for heating and hot water in buildings, showing a decrease in both PE consumption and CO 2 emissions, even if the hydrogen is obtained from natural gas reforming. However, this PE reduction is directly related to the thermal energy conversion efficiency of the CHP and the boiler because in the best situation a 50% PE reduction can be achieved with an energy production of ca. 20% of thermal demand and ca. 50% of the electrical demand. When the fuel cell-based CHP systems are powered with carbon-free hydrogen, the PE reduction is higher when the system is able to meet a big share of the energy demand, which corresponds to a better fit of the heat-to-power ratio between production and demand. The use of micro-CHP units integrated into smart grids can help to reduce not only the thermal and electrical demand of the user but also the electrical demand from the nearby with the proper energy management. The economic viability of fuel cell-based CHP units is similar to other technologies such as solar thermal systems that are projected to supply a maximum share of the thermal demand, ensuring the higher possible operating time. Based on the results of Figure 12,
Sustainability 2021,13, 1776 17 of 19 the optimal situation corresponds to centralized systems where the total operating time is above 80% of the year-hours and the thermal demand can be fully supplied. Author Contributions: The first author, J.R., has taken lead on all the steps of the research and writing process. The rest of authors have contributed as follow: research methodology, F.S., A.L. and F.B.; simulation, V.G., L.D. and A.R.; validation, P.V., A.G.; writing—original draft preparation, F.S., A.L. and F.B.; supervision, F.S. and A.L.; writing—review and editing, F.S., A.L. and F.B. All authors have read and agreed to the published version of the manuscript. Funding: This research was funded by the Secretariat of State for Research of the Spanish Ministry of Economy and Competitiveness (DPI2015-69286-C3-1-R), the Spanish Ministry of Science and Innovation (RTI2018-096001-B-C33), and the Aragon Government (LMP246_18). Institutional Review Board Statement: Not applicable. Informed Consent Statement: Not applicable. Acknowledgments: This work has been partially funded by the Secretariat of State for Research of the Spanish Ministry of Economy and Competitiveness under the project MICAPEM (ref.: DPI201569286-C3-1-R) and by the Spanish Ministry of Science and Innovation under the project DOVELAR (ref.: RTI2018-096001-B-C33). LIFTEC research team would also acknowledge the funded provided by the Aragon Government under the project LMP246_18. Conflicts of Interest: The authors declare no conflict of interest. Nomenclature Abbreviations CHP Combined heat and power system EES Electrical energy storage system EPBD Energy Performance of Buildings Directive (2010/31/EU) HtP Heat-to-power energy ratio PE Primary energy PEMFC Polymer exchange membrane fuel cell TES Thermal energy storage system Variables COCHP 2CO2emissions from the combined heat and power unit (kg) fCO2CO2emissions conversion factor, kg of CO2per kWh of end-use energy fPE Primary energy conversion factor, kWh of primary energy per kWh of end-use energy . QRated thermal power of the combined heat and power unit (kW) Qbackup Back-up heater energy flow (kWh) QDDaily thermal energy demand (kWh) Qfuel Fuel energy flow in the combined heat and power unit (kWh) QCHP Thermal energy produced by the combined heat and power unit (kWh) t Estimated daily operation time of the combined heat and power unit (h) Wbal Electrical energy balance (kWh) WCHP Electrical energy produced by the combined heat and power unit (kWh) WDDaily electrical energy demand (kWh) WExp Net electrical exported energy to the grid (kWh) WImp Net electrical imported energy from the grid (kWh) ηQThermal efficiency to supply the energy demand from the generation ηQ CHP Thermal energy performance for the combined heat and power unit ηW CHP Electrical energy performance for the combined heat and power unit ηWElectrical efficiency to supply the demand from the generation Subscripts e electricity g gas
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