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Article

Sustainability Indicators for the Manufacturing and Use of a Fuel Cell Prototype and Hydrogen Storage for Portable Uses

by
Daniel Garraín
*,
Santacruz Banacloche
,
Paloma Ferreira-Aparicio
,
Antonio Martínez-Chaparro
and
Yolanda Lechón
CIEMAT–Centro de Investigaciones Energéticas, Medioambientales y Tecnológicas, Departamento de Energía, Avda. Complutense 40, E-28040 Madrid, Spain
*
Author to whom correspondence should be addressed.
Energies 2021, 14(20), 6558; https://doi.org/10.3390/en14206558
Submission received: 24 August 2021 / Revised: 28 September 2021 / Accepted: 8 October 2021 / Published: 12 October 2021
(This article belongs to the Special Issue Advances in Portable Technologies for Hydrogen Fuel Cells)
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Abstract

:
A sustainability assessment regarding the manufacturing process and the use of a new proton exchange membrane fuel cell (PEMFC), specially designed for portable hydrogen applications, is presented. The initial fuel cell prototype has been configured by taking into account exclusively technical issues. However, a life cycle analysis considering environmental and socioeconomic impacts is crucial to improve the model to develop a more sustainable product. From the environmental perspective, the durability of the system and its efficiency are key elements required to decrease the potential overall impacts. High electricity consumption for manufacturing requires a commitment to the use of renewable energies, due to the high current value of the projected impact of climate change (42.5 tonnes of CO2 eq). From the socioeconomic point of view, the dependence of imported components required for the synthesis of some materials displaces the effects of value added and employment in Spain, potentially concentrating the largest impact on countries such as Singapore, Japan and the UK, whereas the cell assembly would have a greater benefit for the country of fabrication. These results provide a basis for new research strategies since they can be considered standard values for improving future upgrades of the fuel cell in terms of sustainability.

1. Introduction

Hydrogen technologies are emerging as a good solution for clean and sustainable power generation [1]. Fuel cells and electrolysers can contribute to sustainability by meeting the energy demand in a positive manner [2,3]. Although most research efforts in relation to fuel cells are concentrated on stationary and transport applications, portable power is progressively attracting more interest [4,5]. The fast-growing power demands of portable electronic devices are hardly satisfied by current battery technology [6]. Ziegler at al. conducted a study showing that from 1991 through 2018, the achievable energy density in batteries rose from approximately 200 W h L−1 to over 700 W h L−1, whereas the initial specific energy of 80 W h kg−1 was more than three-fold higher [7]. After 2002, Li-ion batteries have become the most promising battery technology for portable electronic devices [8].
Lithium-ion batteries are under constant development, but they still have some issues. One of these is the use of cobalt in the cathode, the production of which raises environmental and social concerns in producer countries [9]. Alternative elements such as nickel and manganese are also considered, but cobalt is still used in most batteries [10]. Lithium, on the other hand, is mainly produced in Australia, although Chile has larger reserves that cannot be mined. They must be extracted from the ground by pumping water into the earth, a process that is considered to negatively impact the environment [11]. In addition, recycling is an important aspect, considering the limited lifetime of batteries’ components. The current recycling processes of lithium batteries produce more emissions than the production of new ones. As a result, re-use is considered preferable to recycling in the waste management hierarchy in order to extract maximum economic value and minimize environmental impacts [12]. As their market continues to grow, batteries are typically replaced when they degrade to about 80% of their original capacity in demanding applications, such as electric vehicles [13,14]. Although unsuitable for them, these batteries are very cost-effective for other applications, and re-use lifetimes in the range of 10 years have been estimated [15].
Despite the significant advances attained for batteries over years in terms of energy density, efficiency, durability, and safety, there is may be an inability for batteries to cope with the increasing demands of modern electronic equipment. With the rapid evolution of the portable electronics market, further advances in rechargeable batteries are expected for years to come. It has been speculated that existing batteries, including Li-ion batteries, have limited room for further improvement and that new electrochemical reactions are required to achieve a breakthrough in increasing the battery energy density [16,17,18,19].
Batteries with larger capacity are currently required in order to satisfy the increased safety requirements and power consumption of newly developed applications. Despite the advances achieved, the performance of current batteries still falls short of the demands of consumers [20]. Researchers involved in the development of future batteries hope that they can achieve energy densities two to five times higher than those currently available [21,22]. The future of power sources for these appliances will have to combine high power density, increased energy density, reliability, and short charging times [23].
The competition between the different technologies in this sector will be driven by smaller, cheaper, and lighter portable electronic devices with an increasing number of functions. These new products offer a multitude of features, including connectivity, enterprise, and multimedia capabilities. Wearable electronic devices incorporating the body’s sensing, communication, and digital entertainment functions (i.e., smart watches, smart glasses, smart clothing, heart rate monitors, and fitness trackers) and unmanned aerial vehicles such as consumer drones with endless potential applied to power patrol, movie-video shooting, mobile communication, meteorology monitoring, or express delivery, creating demand for the development of new power units with a larger capacity to satisfy the increased safety requirements and power consumption. Fuel cells present a number of advantages over batteries since they provide longer operating times, wider temperature ranges, reduced environmental issues associated with disposal, and instantaneous recharge [1]. However, small portable devices are finding some technical hurdles to adapt fuel-cell-based power units to their structure due to the complexity of the auxiliary components of the fuel cell system and the low energy density of current PEMFC models [4]. A recently patented portable fuel cell model (ES1232498U, WO2020240063A1) has been especially designed for completely passive operation with minimal auxiliary systems [24]. Some of the materials used for its manufacture could be carefully selected among a number of compounds of similar properties, in the search for a more sustainable and environmentally friendly product.
Several publications indicate that fuel cells entail environmental benefits, but also exert a certain impact on the demand for non-renewable resources, in particular for so-called specialty or technology metals. Platinum is a matter of particular concern. Nowadays, PEMFC vehicles contain more platinum than combustion engine vehicles by a factor of >10; thus, although new cells operating at higher temperature (HT-PEMFCs) reduce their Pt loading requirements, their widespread deployment could severely aggravate the temporal and structural scarcity that is already perceptible in the global platinum market [25]. Current recovery technologies for valuable materials from fuel cells are mainly focused on the recovery of precious metals through conventional hydrometallurgical and pyro-hydrometallurgical pathways, although novel processes are being developed to recycle other relevant materials, such as carbon support and the use of ionomers from membrane-electrode assemblies [2]. As a matter of fact, the disposal and recycling of per- and polyfluoroalkyl substances such as those used as electrolytes (Nafion) in proton exchange membrane fuel cells (PEMFCs), commonly known as PFAS, are a matter of increasing concern, since all those substances are considered to be persistent in the environment, also implicating adverse health outcomes [26]. The monitoring of waste streams for PFAS; stopping PFAS discharges into water, soil, and air; and protecting the health of fence-line communities close to the waste disposal sites are essential to mitigating the impacts of PFAS pollution on human health [27].
In 2020, an international partnership financed by the European Union initiated the BEST4Hy H2020 projects to develop technologies for the recovery of critical raw materials from hydrogen technologies [28]. Novel recovering technologies provide enhanced techno-environmental performance and safer operating conditions. However, further efforts are needed to reach maturity in these processes, which depends not only on technical aspects but also on the regulatory framework and the level of deployment of hydrogen fuel cell products.
Different environmental studies based on life cycle assessments (LCAs) of hydrogen fuel cells have been found in the literature. Pehnt, one of the most referenced authors of LCAs of fuel cells, carried out a complete LCA of fuel cell system components and found that this technology offers numerous advantages in terms of different environmental impacts [29] such as those related to greenhouse gases (GHG) and particle emissions. Valente and collaborators have recently published the most remarkable and interesting studies about LCA approaches on hydrogen options [2,30,31,32,33,34,35,36,37,38]. More specifically, Wulf and Kaltschmitt [39] developed an LCA about the supply of hydrogen and highlighted that the electrolysis used for producing hydrogen reduces GHG emissions only if the electricity comes from renewable sources compared to fossil fuel sources. Ally and Pryor [40] performed an LCA of diesel, natural gas, and hydrogen fuel cells for transportation systems and found that hydrogen fuel cells could compete with the others, since they can attain similar power although most of the impacts are lessened. Bicer and Dincer [41] analysed different aviation fuels, concluding that ammonia and hydrogen-based fuel could strongly reduce the environmental impact. Mori et al. have recently reported relevant data on materials that are the most commonly used in fuel-cell and hydrogen technologies in a criticality and life cycle assessment [42]. Finally, a study from Garraín and Lechón [43] highlighted the environmental benefits of recycling the main metals, such as platinum, tin, copper and aluminium, of a PEMFC supplied by hydrogen in a cargo-bike. Most of the LCA studies related to fuel cell technology are devoted to fuel cell electric vehicles (FCEVs) in comparison to those powered by batteries (BEVs) [44,45,46]. However, smaller applications powered by portable fuel cells have been scarcely studied to date.
Regarding socioeconomic studies, fuel cells are usually assessed with a focus on transport applications [47], usually considering capital expenditures (CAPEX) and operating expenditures (OPEX) costs to perform a cost-benefit analysis (CBA) [48] or both LCA and life cycle cost (LCC) studies [49]. Mehmeti and colleagues performed an LCA on fuel cells, pointing out the relevance of economic criteria in the decision-making progress and the need to employ comprehensive dynamic multi-criteria environmental impact analysis coupled with economic aspects, to allow a robust comparison of results [50]. Estimating the total, direct, and indirect effects of fuel cells on economic growth and employment through the input-output approach would enrich the sustainability assessment. To our knowledge, no economic assessment of fuel cells has been undertaken in regard to this methodology.

2. Objective

The objective of this study was to assess the behavior of the manufacturing process and the use of a new, recently patented (ES1232498U) portable fuel cell prototype from a sustainability perspective. This model is representative of a new generation of fuel cells specially designed for small devices, which are currently under development. It is therefore an original and pioneering study for the development of new disruptive PEMFC models for portable applications, which is aimed at presenting several environmental and socio-economic quantitative indicators. These results will be considered as standard values for improvements in future upgrades of the fuel cell prototype.

3. Technical Description of the Fuel Cell

The new PEMFC is a development intended to attain power densities comparable with modern Li-ion batteries in portable applications where conventional PEMFCs cannot operate. As a difference from a conventional PEMFC prototype, the developed cell works with fully passive feeding, instead of convective feeding, which decreases the power delivered but improves the overall power density of the system.
The fuel cell has a modified design, aiming to improve the portability of a power production device based on hydrogen [24]. An exploded view of the cell is shown in Figure 1a and a photograph of a cell of 5 cm in diameter (3 cm in diameter for circular electrodes with an active area of 7.1 cm2) is presented in Figure 1b. The anode, where hydrogen reacts, is based on a gas-diffusion electrode (GDE) with a nickel grid as current collector and a polyether ether ketone (PEEK) end-plate with hydrogen inlet and outlet ports. It is able to operate under full dead-end conditions, i.e., without any purging, thanks to a water-permeable window implemented at the back of the anodic plate which is able to permeate the excess water. By these means, the cell attains 100% faradaic efficiency, which means that all the stored hydrogen is used to produce the electric current without wastage. The cathode is an open-air, air-breathing cathode, based on a GDE, a nickel grid current collector, and a columnar aluminum plate opened to the ambience. The electrolyte is a Nafion-based proton exchange membrane (PEM), typically Nafion 212NR (Ion Power).
Gold-coated nickel grids are used as current collectors in this type of air-breathing fuel cell to allow for the rapid entrance of environmental air by natural convection and without forced ventilation. They also provide a good solution through the use of light plastic plates at the anode. Nickel is a good conductor and a relatively cost-effective material. In case of the oxidation of this substrate due to gold-coating defects or pores, nickel forms a passivating oxide that limits the release of nickel ions to the electrodes [51]. The presence of free cations in the cell could contribute to poisoning the proton exchange membrane or the ionomer in the electrodes and reducing the proton conductivity and therefore the cell performance [52].
The cell is able to operate under passive conditions; therefore, no convective forces are necessary for reactant gases during power production, and the system delivers up to 0.14 W cm−2, referring to the active area (Figure 1d). The hydrogen fuel cell system is completed with a hydrogen storage system connected to the cell by means of a pressure regulator (0.8 bar), as shown in Figure 1c. The hydrogen storage system considered in this analysis is based on a commercial metal-hydride canister with a storage capacity of 1 g H2 at 30 bar pressure (Hydrostik Pro) that can be refilled by means of a laboratory electrolyzer. This hydrogen reservoir provides energy for 15 W h consumption, considering a total fuel cell conversion efficiency of 50%. This hydrogen storage element has been considered for the analysis of the complete system, although it could be replaced by other H2 storage and dispensing systems without affecting the fuel cell prototype.

4. Material and Methods

4.1. Life Cycle Assessment

One of the tools most widely accepted by the scientific community to assess the potential environmental impact is the LCA, an analytical procedure that assesses the complete life cycle of a service, process or product, regulated by the International Organization for Standardization (ISO) standards [53,54]. The main stages in the methodology are: definition of the goal and scope, the life cycle inventory (LCI), the life cycle impact assessment (LCIA), and interpretation of the results.
The goal of this study is to develop environmental indicators of the manufacturing and use stages of the new PEMFC through an attributional LCA approach. Then, the end-of-life stage is excluded. The manufacturing processes of each material have been included and transports are excluded because of their negligible value. The functional unit for presenting the results is the consideration of the useful life of the PEMFC. Figure 2 shows the system’s boundaries, including the inputs and the considered stages of the process.
In order to carry out the material inputs to fulfil the LCI analysis, the second stage of the LCA methodology, it is necessary to consider the fuel cell and the hydrogen reservoir. As previously described in Section 3, the fuel cell can be divided into the anode, the membrane, and the cathode. It is also necessary to consider the cell locks, and the gas connectors. Table 1 shows the main materials for manufacturing the fuel cell of 1 W power. The values used were the most up-to-date values in the database, in which data before 2010 have not been considered. Table 2 shows the inventory source of each material, in which PEEK was characterized.
On the other hand, the hydrogen reservoir consists of a commercial metal-hydride storage system. It is a cylinder with 5 g of aluminum coating, and 99 g of a metal hydride (LaNi5), which may absorb up to 1 g of hydrogen at room temperature, which is equivalent to 15 W h of net electricity produced by the fuel cell (50% efficiency is assumed, according to personal communications from the technical staff). The hydrogen can be produced by a laboratory-scale hydrolyzer with the following characteristics: 3 L h−1, 20 W, and 70% efficiency. The fuel cell power may attain up to 40,000 h of lifetime if operated in constant current load, but the durability decreases to approximately 5000 h under variable power production due to accelerated degradation by start-up and shut-down events, and to fast changes in the power demand.
Based on an LCA approach, the European Commission (EC) developed a harmonized impact assessment method called the environmental footprint (EF) for both products and organizations [55]. EF provides a method for modelling the environmental impact of material and energy flows and emissions and waste flows associated with a product throughout its life cycle. In addition, it ofers guidance on how to establish methodological requirements for specific categories of products intended for use in the Product Environmental Footprint Category Rules (PEFCR). These impact categories are generally related to the use of resources and the emissions flows affecting both human health and ecosystems. The EF guide recommends the categories developed using the International LifeCycle Datasystem (ILCD) 2011 midpoint method [56].

4.2. Multi-Regional Input-Output Assessment

The input-output methodology [57] has also been used to estimate the impacts that the fuel cell investment could have in terms of economic growth (value added) and employment creation. This methodology uses input-output tables, a macroeconomic tool which describes the sale and purchase relationships between producers and consumers within an economy. The input-output methodology allows the estimation of the total (direct and indirect) economic stimulation produced by an increase in the demand for goods and services. Moreover, socioeconomic impacts such as value added and employment can be addressed, pointing out the country and sector origin where economic effects are being produced. Working with multi-regional input-output tables (MRIOT), the trade interdependence among sectors and countries can also be captured [58].
For this analysis, the Organization for Economic Cooperation and Development’s inter-country input-output (OECD-ICIO) tables [59] have been used, in view of the most recent edition based on International Standard Industrial Classification (ISIC) Revision 4 [60]. This database provides a time series of 69-region and 36-sector symmetric industry-by-industry MRIOTs with matching employment satellite accounts [61]. The present study aggregates the MRIOTs for the year 2015 into seven regions (Spain, Germany, the UK, Japan, Singapore, the United States and the rest of the world), considering the countries that are directly involved in the manufacturing of the components needed for assembling the fuel cell. The impacts calculated are expressed by the following matrix equation:
F H = f ^   I − A − 1 Y H
where FH indicates the total socioeconomic effects (value added and employment) of investing in the fuel cell, f ^ denotes the diagonalized socioeconomic vector (value added/employment per unit of output), (I − A)−1 is the Leontief inverse, and YH represents the direct investments (components) of the fuel cell. The Leontief inverse can be understood as the multiplier effect and provides information about the total stimulation produced from both direct and indirect effects produced by each direct monetary unit invested in the project [62]. This approach has been widely used in assessing energy investments at a country-level [63] or considering commercially feasible investments that account for considerable amounts of money [64]. However, it is not common to apply this methodology to early-stage science-driven prototypes, as could be the case for the portable fuel cell in this study. Hence, the results here must be addressed carefully. However, this methodology has the advantage of identifying global value chains and the indirect impacts that arise as a carry-over effect.
In this analysis, the hydrogen fuel cell of 1 W power has been considered. The material cost data of the manufacturing phase using prices from commercial suppliers in Madrid (Spain) are shown in Table 3, as well as the corresponding origin country.
Once material costs have been accounted for, the investments needed to produce the fuel cell (final goods and services required) are allocated to the corresponding economic sectors and countries on the input-output table (i.e., the gas connectors produced in Japan are included in the computer, electronic, and optical products sector). This allows us to construct the demand vector, which correspond to the direct effects, which will be later used to calculate the indirect effects. Table 4 shows the final demand vector, which is the total investment costs assigned to the corresponding economic sectors of each country. Costs have been converted into USD and brought to 2015 prices.
Once the demand vector is constructed, it can be multiplied by the Leontief inverse matrix to obtain the indirect effects, estimating the total demand of goods and services of each phase.

5. Results and Discussion

5.1. Environmental Indicators

Table 5 shows the total environmental impact of both the fuel cell and the hydrogen cartridge when the total useful life is considered, according to the LCIA stage of the LCA methodology. Due to the high number of hydrogen cartridges consumed, the influence of the infrastructure is less than 1% in the majority of impact categories. Nevertheless it is important to take into account an exploratory analysis of this subject in order to identify the hotspots for improving new materials. Figure 3 shows the contribution of each part in the impact categories. Anodes are the main contributors to the EF because of their composition. Anodic plates are made of PEEK, a material of which the production is nowadays highly electricity-consuming because it must be manufactured at the lab-scale. The electricity consumption of the PEEK manufacturing process is expected to be optimized when produced at the market-scale and additionally the electricity generation mix is expected to be further decarbonized in the future. Both factors will lead to a decrease in the EF results. Additionally, further modifications of the hydrogen-powered fuel cell prototype could also consider using alternatives to these elements to develop a power unit with the lowest possible EF.
Figure 4 shows the EF percentages and composition of the cartridge and the hydrogen stored within it. The major impact from the cartridge is attributed to the metal hydride because of the higher amount of aluminum. Aluminum production is also very energy-intensive. The electricity consumption in aluminum production has been reduced in recent years and is expected to be further optimized. Additionally, electricity mixes around the world will increasingly make use of renewable energies, reducing the overall EF of the cartridge.
The environmental effects of the hydrogen supply are due to the high amount of electricity consumed by the electrolyzer during the generation process, due to its small scale for domestic use. However its EF would depend on the region of the world where the system was recharged.
On the other hand, electricity consumption associated with the manufacturing stage of the prototype is a very important hotspot, which is largely affected by the laboratory-scale production of the initial model.

5.2. Socio-Economic Indicators

The multiplier effect on the production of one fuel cell in the priority country (Spain) is estimated to be 2.42 times the effect on the demand for the components. However, socioeconomic effects of the manufacture of this fuel cell would mainly have an impact abroad, both in terms of economic growth and employment, due to the special technology required for the production of new materials and import dependency of the components (i.e., the hydrogen container). The global value chain (GVC) phenomenon, where a final product is created across different countries, determines the functioning of production processes nowadays, with impacts on value added and job creation. In this study, domestic manufacturing of components accounts for 6.5% of the initial investment. However, other actors arise when considering a boost in production, value added, and jobs, displacing Spain’s participation. Only 5.6%, 4.5%, and 2.4% of the effects would have an impact domestically, respectively. The initial investment depends on imported components and this is more severe when looking at value adding and especially at employment (see Figure 5).
The main economic sectors responsible for the largest shares of the three types of socioeconomic effects analyzed are displayed in Figure 6. Singapore becomes the most benefited country, where value added and employment are created in electrical equipment activities related to the hydrogen metal-hydride container, which has been considered here as hydrogen storage medium, although possible alternatives could also be considered. Many relevant sectors and regions where no initial investment has been made become important providers of intermediates and appear to benefit the most in terms of production, value added and employment (sectors shown in bold) due to GVC: extractive activities coming from the “rest-of-the-world” region need to be performed to produce the intermediates required for the final components.

6. Conclusions

First, the environmental and socioeconomic results of the manufacturing and use stages of a new portable fuel cell prototype, according to the utility model ES1232498U, using hydrogen fuel have been presented.
By considering the manufacturing of a Spanish H2-fuel cell system for the portable devices analyzed, it can be concluded that hydrogen supply and storage is the most critical element in the power system.
The electrolyzer used for the hydrogen supply has been considered to work with the Spanish electricity mix, which still uses some fossil technologies. The expected full decarbonization of the electricity production in Spain (and in Europe) by the midcentury will decrease the environmental impacts associated to the production of hydrogen for the fuel cell to a large extent. It would also be possible that the device could be operated using only a renewable energy source, thus reducing the environmental impacts.
The EF of the cartridge production can also be greatly reduced if renewable electricity is used in the aluminum production process.
Regarding the manufacturing of the fuel cell, the anodic plates, which are made of a high-performance engineering plastic with outstanding resistance to harsh chemicals, and excellent mechanical strength and dimensional stability, are the main contributors to the environmental footprint. Consequently, further modifications of the hydrogen-powered fuel cell prototype will consider using alternatives to these elements to develop a power unit with a small EF and positive impacts in domestic added value, manufacturing, and job creation.
Overall, there are many avenues for EF reductions in the manufacturing and use of the analyzed H2 fuel cell system for portable devices. In order to decrease the high electricity consumption required for the manufacturing process, a future potential (semi)industrial-scale process could improve the efficiency of the system and reduce its impacts. Additionally, the abovementioned decarbonization of electricity production will also contribute to reducing these impacts. In the use of the cell, the assumption of 5000 h of useful time is considered a pessimistic scenario for the first prototype, so it would be necessary to improve its durability and its efficiency in order to decrease all of its potential impacts.
From the socioeconomic perspective, the fragmentation of production among countries determines the benefits in terms of value added and employment creation. In this case, the high dependency on imported components undermines the domestic value added and the employment creation that are produced in the manufacturing countries. Ceteris paribus, jobs related to the fuel cell assembly process remain the only option to boost employment domestically. For the PEMFC-producing country, it could be convenient to address this problem through policies to boost the manufacturing of components locally (i.e., fostering a home-grown industry or searching for substitute components), thus benefitting to a higher extent by retaining more value added and jobs.
There is no possibility of comparing the quantitative results of the developed indicators with other fuel cells due to their small scale and exclusive function. Nevertheless, new developments and improvements will be carried out in a follow-up project for portable applications, intending to improve the power density and reliability of the cells, considering the results of this analysis.

Author Contributions

Conceptualization, D.G. and S.B.; methodology, D.G. and S.B.; formal analysis, D.G. and S.B.; investigation, D.G., S.B., and Y.L.; resources, P.F.-A. and A.M.-C.; data curation, P.F.-A. and A.M.-C.; writing—original draft preparation, D.G., S.B., P.F.-A., and A.M.-C.; writing—review and editing, Y.L.; visualization, D.G.; supervision, Y.L.; project administration, P.F.-A. and A.M.-C.; funding acquisition, P.F.-A. and A.M.-C. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Spanish Ministry of Science and Innovation by means of the ELHYPORT project (PID2019-110896RB-I00), a four-year project.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

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Energies 14 06558 g001 550
Figure 1. (a) Exploded view of the portable PEMFC; (b) front view of the cell (5 cm diameter); (c) view of the cell and hydrogen cartridge for portable applications; (d) stabilized polarization curve and power delivered.
Figure 1. (a) Exploded view of the portable PEMFC; (b) front view of the cell (5 cm diameter); (c) view of the cell and hydrogen cartridge for portable applications; (d) stabilized polarization curve and power delivered.
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Figure 2. PEMFC system boundaries considered in the LCA.
Figure 2. PEMFC system boundaries considered in the LCA.
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Figure 3. Relative contribution to the EF of the different components of the fuel cell of 1 W power.
Figure 3. Relative contribution to the EF of the different components of the fuel cell of 1 W power.
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Figure 4. Relative contribution to the EF of the hydrogen cartridge and supply.
Figure 4. Relative contribution to the EF of the hydrogen cartridge and supply.
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Figure 5. Socioeconomic impacts. The initial investment (understood as final demand) increases across the countries (via intermediates), adding value and generating employment throughout all the stages of production.
Figure 5. Socioeconomic impacts. The initial investment (understood as final demand) increases across the countries (via intermediates), adding value and generating employment throughout all the stages of production.
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Figure 6. The main economic sectors responsible for the largest shares of socioeconomic effects.
Figure 6. The main economic sectors responsible for the largest shares of socioeconomic effects.
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Table
Table 1. LCI of the fuel cell infrastructure.
Table 1. LCI of the fuel cell infrastructure.
PartComponentMaterialWeight (g)
AnodeAnodic plate 1PEEK6.567
Anodic plate 2PEEK9.175
Membrane 1Nafion (Nf117)0.305
Junction 1Silicone0.079
Lock 1Stainless steel (screws and washers)2.183
Junction 2Silicone0.283
Junction 3Silicone0.497
Frame 1PET-G (20% carbon fiber)1.162
Grille 1Nickel0.397
Electrode 1Charcoal cloth + Pt (Pt/C)0.151
MembraneMembrane 2Nafion (Nf112)0.293
CathodeJunction 4PET film (Mylar®)0.069
Electrode 2Charcoal cloth + Pt (Pt/C)0.156
Frame 2PET-G (20% carbon fiber)1.161
Frame 3Aluminium2.278
Grille 2Nickel0.399
Cathodic plateAluminum17.086
Cell locksLock 2Steel8.060
Lock 2Steel2.513
Gas connectorsTwo gas connectorsReinforced glass fiber5.424
Table
Table 2. Inventory sources considered for the materials.
Table 2. Inventory sources considered for the materials.
MaterialInputDatabase
PEEKHydroquinone, RER, prod, Alloc DefEcoinvent
Potassium carbonate, at plant GLOEcoinvent
Toluene, at plant, RERIndustry data 2.0
Electricity, med volt, prod ES, at gridEcoinvent
Natural gas, burned, ESEcoinvent
Benzyl chloride, at plan, REREcoinvent
Chlorine gas, production mix, RERAgri-footprint
Aluminium, primary, ingot, GLO, Alloc EnEcoinvent
Hydrochloric acid, 36% in H2O, from reacting propylene and chlorine, at plant, REREcoinvent
Aniline, at plant, REREcoinvent
Lead, primary, at plant, GLOEcoinvent
Sodium hydroxide, 50% in H2O, production mix, at plant, REREcoinvent
Nitric acid, ETHETH-ESU
Ammonia, liquid, at reg storehouse, CHEcoinvent
Boric acid, anhydrous, at plant, REREcoinvent
Hydrogen fluoride, at plant, GLOEcoinvent
NafionTetrafluoroethylene, at plant, REREcoinvent
SiliconeSilicone product, at plant, REREcoinvent
Stainless steelX12Cr13 (416) IIDEMAT
Hot rolling, steel, REREcoinvent
PET-GPolyethylene terephthalate (PET) granulate, production mix, at plant, amorphous, RERELCD
Carbon fiber IIDEMAT
NickelNickel, 99.5%, at plant, GLOEcoinvent
Charcoal clothPhosphoric acid, industrial grade, 85% in H2O, at plant, REREcoinvent
Textile, woven cotton, at plant, GLOEcoinvent
SteelReinforcing steel, at plant, REREcoinvent
Rolling steel IIDEMAT
Glass fiberGlass fibre reinforced plastic, polyester resin, hand lay-up, at plant, REREcoinvent
Extrusion, plastic pipes, REREcoinvent
Table
Table 3. Investment cost disaggregation and supplier countries.
Table 3. Investment cost disaggregation and supplier countries.
ComponentInvestment Cost BreakdownCountry€2018
Cell 34.15
PEEKUK11.76
Nickel gridUnited States0.70
SteelSpain0.10
SiliconeSpain0.10
Gas diffusion electrode (Pt/C)United States4.00
MembraneUnited States4.55
ScrewsSpain0.08
WashersSpain0.08
NutsSpain0.08
M2 screwsSpain0.08
M2 washersSpain0.08
Stainless steel (Helicoil®)Spain2.32
Gas connectors (2)Japan5.20
Aluminium dissipaterGermany5.01
Hydrogen Metals-Hydride Container (H2 reservoir)Singapore40.00
Portable System 47.00
Pressure controlJapan22.00
Conduits and connectorsSpain5.00
DC-DC conversionUK22.00
TOTAL 121.15
Table
Table 4. Demand vector.
Table 4. Demand vector.
CountrySectorInvestment Costs ($2015)
SingaporeElectrical equipment46.01
JapanComputer, electronic and optical products31.29
UKElectrical equipment23.01
UKChemicals and pharmaceutical products13.53
United StatesElectrical equipment9.84
GermanyElectrical equipment5.76
SpainElectrical equipment5.75
SpainBasic metals2.78
United StatesBasic metals0.81
SpainFabricated metal products0.46
SpainChemicals and pharmaceutical products0.12
Table
Table 5. EF results of the manufacturing and useful life of the fuel cell and the percentage contributions of the fuel cell infrastructure versus hydrogen cartridges.
Table 5. EF results of the manufacturing and useful life of the fuel cell and the percentage contributions of the fuel cell infrastructure versus hydrogen cartridges.
Impact CategoryUnit *Total Value% Fuel Cell% Cartridges
Climate change (CC)kg CO2 eq42,5000.1999.81
Ozone depletion (OD)kg CFC-11 eq0.150.1199.89
Human toxicity, non-cancer effects (HHnc)CTUh3.7 × 10−30.4799.53
Human toxicity, cancer effects (HHc)CTUh7.8 × 10−40.1699.84
Respiratory inorganics, particulate matter (RI)Disease incidence1.4 × 10−30.2199.79
Ionizing radiation (IR)kBq U235 eq18,8000.0499.96
Photochemical ozone formation (PO)kg NMVOC eq135.50.1799.83
Acidification (AC)molc H+ eq4430.1199.89
Terrestrial eutrophication (EuT)molc N eq4610.1799.83
Freshwater eutrophication (EuF)kg P eq200.0899.92
Marine eutrophication (EuM)kg N eq450.1599.85
Freshwater ecotoxicity (EcF)CTUe16,5000.2799.73
Land use (LU)Pt33,4000.1299.88
Water scarcity (WS)m3 water world eq1.19 × 107
1.2 × 107		0.0899.92
Resource use (mineral and metals) (Rmm)kg Sb eq0.054.8295.18
Resource use (energy and fossils) (Ren)MJ6.26 × 105
6.3 × 105		0.1999.81
* CTUh,e: Comparative toxic units (human, ecosystem).
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Garraín, D.; Banacloche, S.; Ferreira-Aparicio, P.; Martínez-Chaparro, A.; Lechón, Y. Sustainability Indicators for the Manufacturing and Use of a Fuel Cell Prototype and Hydrogen Storage for Portable Uses. Energies 2021, 14, 6558. https://doi.org/10.3390/en14206558

AMA Style

Garraín D, Banacloche S, Ferreira-Aparicio P, Martínez-Chaparro A, Lechón Y. Sustainability Indicators for the Manufacturing and Use of a Fuel Cell Prototype and Hydrogen Storage for Portable Uses. Energies. 2021; 14(20):6558. https://doi.org/10.3390/en14206558

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Garraín, Daniel, Santacruz Banacloche, Paloma Ferreira-Aparicio, Antonio Martínez-Chaparro, and Yolanda Lechón. 2021. "Sustainability Indicators for the Manufacturing and Use of a Fuel Cell Prototype and Hydrogen Storage for Portable Uses" Energies 14, no. 20: 6558. https://doi.org/10.3390/en14206558

APA Style

Garraín, D., Banacloche, S., Ferreira-Aparicio, P., Martínez-Chaparro, A., & Lechón, Y. (2021). Sustainability Indicators for the Manufacturing and Use of a Fuel Cell Prototype and Hydrogen Storage for Portable Uses. Energies, 14(20), 6558. https://doi.org/10.3390/en14206558

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