Literature DB >> 33803681

Polymer Membranes for All-Vanadium Redox Flow Batteries: A Review.

Dennis Düerkop1, Hartmut Widdecke1, Carsten Schilde2, Ulrich Kunz3, Achim Schmiemann1.   

Abstract

Redox flow batteries such as the all-vanadium redox flow battery (VRFB) are a technical solution for storing fluctuating renewable energies on a large scale. The optimization of cells regarding performance, cycle stability as well as cost reduction are the main areas of research which aim to enable more environmentally friendly energy conversion, especially for stationary applications. As a critical component of the electrochemical cell, the membrane influences battery performance, cycle stability, initial investment and maintenance costs. This review provides an overview about flow-battery targeted membranes in the past years (1995-2020). More than 200 membrane samples are sorted into fluoro-carbons, hydro-carbons or N-heterocycles according to the basic polymer used. Furthermore, the common description in membrane technology regarding the membrane structure is applied, whereby the samples are categorized as dense homogeneous, dense heterogeneous, symmetrical or asymmetrically porous. Moreover, these properties as well as the efficiencies achieved from VRFB cycling tests are discussed, e.g., membrane samples of fluoro-carbons, hydro-carbons and N-heterocycles as a function of current density. Membrane properties taken into consideration include membrane thickness, ion-exchange capacity, water uptake and vanadium-ion diffusion. The data on cycle stability and costs of commercial membranes, as well as membrane developments, are compared. Overall, this investigation shows that dense anion-exchange membranes (AEM) and N-heterocycle-based membranes, especially poly(benzimidazole) (PBI) membranes, are suitable for VRFB requiring low self-discharge. Symmetric and asymmetric porous membranes, as well as cation-exchange membranes (CEM) enable VRFB operation at high current densities. Amphoteric ion-exchange membranes (AIEM) and dense heterogeneous CEM are the choice for operation mode with the highest energy efficiency.

Entities:  

Keywords:  all-vanadium redox flow battery; costs; current density; efficiency; polymer membrane

Year:  2021        PMID: 33803681      PMCID: PMC8003036          DOI: 10.3390/membranes11030214

Source DB:  PubMed          Journal:  Membranes (Basel)        ISSN: 2077-0375


1. Introduction

The growing use of renewable energy supplements fossil fuel and nuclear power in many parts of the world with considerable proportions [1,2]. The expansion of the electrical grid and the efficient use of fluctuating energies still pose challenges, which are fundamentally associated with costs. In addition to lithium-ion batteries, flow-batteries have increasingly gained interest. Redox flow batteries have external tanks to store electric energy in vanadium-based electrolytes. The electrolytes are pumped through the battery stack for energy conversion (charging or discharging). This is the main advantage of flow batteries. The power depends on the stack size and the capacity on the volume of the tanks. The intermediate storage of electrical energy in all-vanadium redox flow batteries (Figure 1) is being pursued seriously and is demonstrated in numerous pilot projects and industrial installations (e.g., cellcube [3], Rongke Power [4], Sumitomo Electric [5], Fraunhofer ICT [6]). These highly efficient electrochemical storage units can generally be industrially manufactured in large quantities [7,8,9]. Its intended use can be either as part of large-scale plants or for consumer use in smaller applications. Studies on techno-economic assessment of VRFB are analyzed in [10]. As a result, guide values of 650 EUR (kWh)−1 and 550 EUR (kWh)−1 for VRFB systems in a power range of 10–1000 kW providing electrical energy for 4 h and 8h are derived from literature. Here, the key components of the electrochemical cell, the active species vanadium, the membranes, the electrode felts and bipolar plates differ in proportion to the total system costs. The proportion of Vanadium costs, membrane costs and electrode felt/bipolar plate costs to total system costs is about 30–60%, 3–30% and below 5%.
Figure 1

Schematic of the all-Vanadium redox flow battery (left charging/right discharging).

Cost reduction is one way to realize marketable products. As an integral part of the VRFB, the membrane influences investment costs, service life and battery performance. Perfluorosulfonic acid (PFSA) membranes account for about 40% of the investment costs of a VRFB stack. Like other VRFB components, the membrane influences the efficiency and power of the cells. Looking at membrane development as a way to optimize costs, these could be reduced by making cheaper membranes available on the market. The costs consist of the specific cost of raw materials, the manufacturing process and, in particular, on the quantity produced. Generally, high proton conductivity and high H+/V selectivity are the main issues to overcome in designing membranes for VRFB. Mechanical and chemical stability (resistance to the highly oxidizing electrolyte of the positive half-cell) during VRFB operation are the main issues membrane materials have to overcome. The development of membrane materials for VRFB has been an ongoing process for decades. From 2011 to 2020, several review papers were published summarizing the most important membrane developments. In [11] Li et al. describe the basic properties of VRFB and its development history. The first demonstration projects are mentioned and the electrical performances and storage capacities achieved are listed. For ion-exchange membranes, requirements and parameters relevant for the operation of the VRFB are described. The production of membranes is also briefly discussed. Furthermore, membrane developments published over a period of about 10 years are listed, differentiating between the various material groups: pore filled membranes; perfluorinated membranes; modified perfluorinated membranes; partially fluorinated IEMs and non-fluorinated membranes. In [12], an overview of membrane properties that are relevant for the VRFB is given. Furthermore, membrane types that can be used in the VRFB are summarized. They are divided into cation-exchange membranes, anion-exchange membranes, amphoteric membranes and non-ionic membranes. H. Prifti et al. [13] provide a brief introduction to the design, manufacture and characterization of ion-exchange membranes. The modification of membranes to improve VRFB performance is discussed and various examples are given. H. H. Cha [14] summarizes the efforts to develop nanocomposite membranes for VRFB. The developments focus on the reduction of vanadium-ion permeability, the improvement of proton conductivity for improved battery performance and a long service life of the battery systems. The focus is on functionalized materials for nanocomposite membranes. The description of membrane properties and the calculation of the coulombic, voltage and energy efficiency are described in detail in previous reviews [11,13,15,16] and are not discussed further here. Table 1 gives an overview of published review papers considering important membrane properties and membranes for redox flow batteries.
Table 1

Overview of review papers considering vanadium redox flow battery membranes.

YearJournalTitleMain FocusRef.
2011Energy Environ. Sci.Ion exchange membranes for vanadium redox flow battery (VRB) applicationall aspects related to IEMsthat are of relevance tounderstand IEMs for VRFB[11]
2011ChemSusChemMembrane Development for Vanadium Redox Flow Batteriesbasic scientific issues associated with membraneuse in VRFBs[12]
2012MembranesMembranes for VRFB Applicationsmembranes for all-vanadium redox flowbattery which has received the mostattention.[13]
2013Electrochimica ActaReview of material research and development for vanadium redox flow battery applicationsa historical overview ofmaterials research anddevelopment [15]
2014Energy Environ. Sci.Anion-exchange membranes in electrochemical energy systemstechnological and scientific limitations and the future challenges related to the use of anion-exchange membranes[16]
2015J.o.NanomaterialsRecent development of Nanocomposite Membranes for Vanadium redox Flow Batteries efforts in developingnanocomposite membranes[14]
2015RSC Adv.Recent development of polymer membranes as separators for all-vanadium redox flow batteriesnew cation exchangemembranes, anion exchangemembranes, amphoteric ionexchange membranes,and non-ionic porousmaterials[17]
2015RSC Adv.A review on recent developments of anion exchange membranes for fuel cells and redox flow batteriesdevelopments in thesynthesis and applications ofAEMs in the field ofelectrochemical energyconversion and storage[18]
2017Chem. Soc. Rev.Porous membranes in secondary battery technologiesunderstanding of thepreparation–structure–performance relationship[19]
2017Journal of Membrane ScienceIon exchange membranes: New developments and applicationsnew iem materials[20]
2018Chem. Commun.Ion conducting membranes for aqueous flow battery systemsporous membranes, differentflow batteries[21]
2018Energy Environ. Sci.Review of electrical energy storage technologies, materials and systems: challenges and prospects for large-scale grid storagestatus and options formechanical,thermal, electrochemical,and chemical energy storage[1]
2018Journal of Membrane ScienceSelectivity of ion exchange membranes: A reviewselectivity of ion exchangemembranes[22]
2019Applied EnergyRecent development of membrane for vanadium redox flow battery applications: A reviewresearch on membranes forVRFB[23]
2019Current Opinion in ElectrochemistryMembranes and separators for redox flow batteriescurrent development trends for membranes and separators for VRFB[24]
2020Journal of Energy StorageMembranes for all vanadium redox flow batteriesdifferent membrane types,membrane performance[25]
2021MembranesPolymer Membranes for all-Vanadium RedoxFlow Batteries: A Review graphical overview ofpolymer membranes; main polymer, impact on VRFBthis paper
Publications of new membranes and their respective tests in VRFB cells have increased significantly since 2012. In addition to the information provided in [11,12,13,14] further developments have been added to the range of membrane types described above. In this review, the basic classification of the membranes into fluoro-carbon, hydro-carbon and N-heterocycle-based membranes is made. They are additionally classified according to their structure and indicated by their chemical character as CEM, AEM, AIEM or non-ionic. The main component of this review is a digest of relevant research results from previous years, too. Thereby, the focus is on membrane main polymers and the impact of new membranes on VRFB performances. Especially, the graphical presentation of the data should provide a comprehensive overview of achievable performance for VRFB cells using different membranes. Knowing that the performance of a VRFB cell is not exclusively dependent on the membrane used, the results are displayed next to each other in order to provide a simplified overview of different membrane types.

2. Commercial Membranes for VRFB

Various companies offer ion-exchange membranes, shown in Table 2, for use in VRFB. Here, the coulombic, voltage and energy efficiencies (CE, VE and EE) are indicated for the respective current densities (CD). These membranes differ in their application for different operating modes, which are divided into energy efficient operation, operation with high current densities and operation with low self-discharge [26]. The “Vanadion” membrane was developed on the basis of Nafion. A thin, more selective Nafion layer was applied to a microporous layer. The membrane is 230 µm thick and provides a constant energy efficiency over 80 charge/discharge cycles [27]. The Nafion membranes N212, N115 and N117 have been commercially available for many years and are often used as reference membranes in comparison to newly developed membrane samples (MS). The measurement results from many studies regarding VRFB efficiencies can be found in Table 3 and Figure 2. More than two decades ago Asahi Glass Co. Ltd. has developed hydro-carbon-based anion exchange membranes with improved chemical stability in VRFB [28,29]. This resulted in the oxidation-stabilized AEM Selemion™ APS4 membrane, which is distributed by AGC [30]. Solvay offered the short side chain PFSA membrane known as Aquivion, which was successfully tested in VRFB [31]. It should be noted that due to different test conditions, the respective efficiency results for the membranes used cannot be compared directly with each other.
Table 2

Overview of commercial membranes for VRFB: (1–9) FumaTech, (10–14) DuPont, (15, 16) Asahi Glass, (17) Solvay.

MSMembraneChemOperating ModeCDCEVEEERef.
mA cm−2%%%
1FAP-330-PEAEMhigh current density20–8095.994.490.5[26]
2FAP-450AEMhigh energy efficiency20–809890.889[26]
3FAP-375-PPAEMlow self-discharging20–809989.989[26]
4FS-930CEMhigh current density20–809694.891[26]
5F-930-RFDCEMhigh current density20–8098.592.491[26]
6F-1075-PKCEMlow self-discharging20–8099.590.590[26]
7F-1850CEMlow self-discharging20–8099.583.483[26]
8VX-20AEMlow self-discharging8099.998484[32]
9Fumapem 14,100CEM-4091.390.282.4[33]
10VanadionCEMhigh current density80889281[27]
11VanadionCEMhigh current density320967673[27]
12Nafion N117CEMhigh current density100966159[34]
13Nafion N115CEMhigh current density80959086[27]
14Nafion 212CEMhigh current density20097.677.976[35]
15New SelemionAEM-4098.687.586.3[28]
16New Selemion CLAEM-6093.587.782[29]
17Aquivion-E87CEMhigh current density80978683[31]
Table 3

The efficiencies of VRFB cells using the listed reference membranes N212, N115 and N117 for investigated current densities.

MSMembraneCDCEVEEERef.MSMembraneCDCEVEEERef.
mA cm−2%%%mA cm−2%%%
18N2122081.29274[37]12N117100966159[34]
18N21280947066[37]52N11740909283[38]
19N21225979592[39]52N117200956663[38]
19N212100979188[39]53N1174093.890.785[33]
20N21250928679[40]54N1175087.682.672.6[41]
21N21250928679[42]55N1175096.59187.5[43]
22N21230609658[44]56N11740919384[45]
22N212607892.371[44]56N117280985453[45]
23N21280----88.8[46]57N11740938983[47]
23N212240----74.8[46]58N11750958783[48]
24N21220----81[49]59N117309076.669[50]
24N21280----71[49]60N117208494.179[51]
25N212200918880[52]60N11780918173.5[51]
26N21280947571[53]61N11720817286[54]
27N21240759571[55]61N11780956666[54]
27N212200928072[55]62N117100966360.5[56]
14N21210095.591.687.5[35]63N11720748167[57]
14N21220097.677.976[35]63N11750837062[57]
64N11760918981[58]
28N1158094.686.682[59]65N11740879280[60]
29N1154094.590.185.2[61]65N117200936863[60]
30N1152092.592.586[62]66N1173096.490.787.4[63]
30N115509482.576[62]67N11720858168.9[64]
31N11520949488[65]67N11780927064.4[64]
31N11510097.577.575[65]68N1175089.990.881.6[66]
32N11540889482[45]69N1175093.890.785[67]
32N115320965654[45]70N1171072.593.868[68]
33N115409494.789[69]70N117608975.367[68]
33N11520097.573.872[69]71N11740948479[70]
34N11520799575[71]72N11730908173[72]
34N11580948479[71]72N1176094.56360[72]
35N11520819173[73]73N117309576.873[74]
35N11580926661[73]73N1171209764.462.5[74]
36N11520908173[75]74N1173090.884.877[76]
36N115100935551[75]75N1176086.380.669.6[77]
37N11520938781[78]76N117509382.377[79]
37N115100976261[78]77N1176092.879.673.8[80]
38N1158094.682.186.8[81]78N11740909283[82]
39N1156091.792.384.7[83]78N117200956663[82]
40N11580----84.5[46]79N11780928780[84]
40N115160----75.2[46]80N11720829074[85]
41N11540987270[86]80N11780927165[85]
42N1158096.648683[32]81N1171072.597.571[87]
43N11580948781.8[88]81N1178092.58478[87]
44N11550978986.3[89]82N11740899181[90]
44N115150987068.6[89]82N117200946763[90]
45N11550968986[91]83N11740909283[92]
46N11540939386.5[93]83N117200956763.7[92]
46N115120968076.8[93]84N1174095.69186.9[94]
47N1154096.2694.390.77[95]85N11740949186[96]
47N11516098.1179.9878.47[95]85N117100968076.8[96]
48N11580938882[97]86N11740959085.5[98]
49N11540919385[99]86N117140967774[98]
49N115160947873[99]87N11720949589.3[100]
50N1155091.391.984[101]87N11780968379.7[100]
51N11580928882[102]88N1174095.989.786[103]
13N11580959086[27]89N11720818772[104]
13N115320976765[27]89N11780946765[104]
90N1172086.290.377.8[105]
Figure 2

Results from VRFB tests using Nafion: (a) current density during cycling tests (b) energy efficiency of VRFB cells at current densities < 100 mA cm−2 and (c) energy efficiency of VRFB cells at current densities ≥ 100 mA cm−2

In VRFB cells, Nafion is suitable as a reference membrane due to its known properties in electrochemical cells and its worldwide availability. Nafion, for example, is preferably used to show the change in battery performance caused by changing the membrane component. Table 3 lists efficiencies measured with different Nafion types as reference membranes for comparison measurements in VRFB cells. N212, N115 and N117 were used in the cycling tests at different current densities. B. Jang et al. [36] describe the influence of Nafion membrane pretreatment on battery performance. The tabular listing of the results shows how efficiencies under different test conditions vary. The lowest energy efficiency of 51% is achieved with N115 (MS34) and the highest energy efficiency of 92% with N212 (MS19). Figure 2a shows the current density used in VRFB cycling experiments with Nafion membranes and the year in which the measurements were published. The numbers close to the data points refer to the sample numbers of the membranes in Table 3. It can be seen that from 2012 onwards cycling tests could increasingly be carried out at current densities greater than 100 mA cm−2. With N212 tests up to a current density of 240 mA cm−2, with N115 tests with a current density up to 320 mA cm-2 and with N117 tests with a current density up to 260 mA cm−2 were performed. This means that progress has been made through cell development in recent years and the research potential does not yet seem to be exhausted. Figure 2b shows the energy efficiency achieved using Nafion membranes at current densities below 100 mA cm−2. The differing VRFB cells and varied test conditions lead to the specific results for each membrane used at the respective current density. For example, energy efficiencies between 66% and 89% could be achieved for the current density of 80 mA cm−2 using N212 membranes, between 61% and 87% for N115 membranes and between 65% and 80% for N117 membranes. At current densities between 20 and 40 mA cm−2, efficiencies of over 90% were measured with N212 and N115. Figure 2c shows the energy efficiencies at current densities of at least 100 mA cm−2 for N212, N115 and N117. While with current densities below 100 mA cm−2 there is no correlation between current density and energy efficiency, with current densities of at least 100 mA cm−2 there is a tendency of decreasing efficiency with increasing current density up to above 200 mA cm−2 for all three membranes N212, N115 and N117. Furthermore, the highest energy efficiencies when using the respective membrane at 100 and 200 mA cm−2 show the increase in efficiency when the membrane thickness decreases:EE (N212) > EE (N115) > EE (N117). Figure 2 clearly shows that the energy efficiency of VRFB cells is related to the membrane used. However, differences in efficiency cannot be exclusively allocated to the specific membrane used due to different cell designs and operation modes of the cells.

3. Polymer Membrane Development

Synthetic membranes are used in various processes such as reverse osmosis, water filtration, dialysis or electrolysis. The respective separation requires membranes with a certain structure and certain chemical properties which result from the specific manufacturing process, formulation conditions and materials used. In electrochemical cells, electrical properties of membranes (membrane/electrolyte) and selectivity are particularly important. VRFB research focuses mainly on polymer membranes due to the generally low material and manufacturing costs involved when produced in large quantities.

3.1. Membrane Structures

Membrane properties not only depend on materials chosen but also on the manufacturing process. The general classification according to their structure and material is shown in Figure 3 [106,107,108]. Whereas dense membranes can be obtained by polymer extrusion or phase inversion by solvent evaporation (e.g., doctor blading) [106,109], porous membranes and separators are made by “stretching” semicrystalline polymer films [106,108]. Other known processes for the production of porous membranes are the sintering of polymer powders, thermal-induced phase separation or diffusion-induced phase separation. Ion-exchange membranes, which are a type of dense membrane, are produced by phase inversion, by solvent evaporation or special polymerization processes with corresponding chemical post-treatment [110].
Figure 3

Classification of synthetic membranes according to their structure.

While several materials are required to prepare a heterogeneous dense membrane, e.g., composite or multilayer membrane, only one polymer or a polymer blend is typically used for homogeneous dense and symmetrically porous membranes. Asymmetrically porous membranes can be prepared from one (integral-asymmetrical) or several polymers (composite-asymmetrical) [107]. In the production of integrally asymmetrically porous membranes, first a thin skin is created on a polymer solution by phase inversion through solvent evaporation. Following this, the remaining solvent is extracted from the polymer solution by immersion in a precipitation bath. With asymmetrical composite membranes, a thin layer (dense or reduced porosity) is applied to a symmetrically porous membrane [107]. Ion-exchange membranes such as Nafion and symmetrically porous membranes such as Daramic have been tested in VRFB for many years. The chemical modification of Daramic by applying charge carriers has resulted in an improvement of the energy efficiency [111]. In this review the membrane structures of published membrane samples are divided into homogeneous dense (dho), heterogeneous dense (dhe), symmetrically porous (sym) and asymmetrically porous (asym) membranes.

3.2. Membrane Polymers

In this review, modified polymer membranes for VRFB are presented from more than 190 publications up to and including the year 2020. In most cases, the developments are based on polymers that can already be produced on a large scale. These include poly(ether ether ketone) (PEEK), poly(sulfone) (PSU), poly(ether sulfone) (PES), poly(phenyl sulfone) (PPSU), poly(vinylidene fluoride) (PVDF), poly(ethylene-tetrafluoroethylene) (ETFE), poly(benzimidazole) (PBI), poly(imide) (PI), perfluorosulfonic acid (PFSA), poly(phenylene ether) (PPE) and poly(tetrafluoroethylene) (PTFE). Other modified membrane polymers investigated include fluorinated poly(arylene ether) (FPAE), poly(fluorenyl ether ketone) (PF), poly(phenylene) (PPh) and poly(phthalazinone ether ketone) (PPEK). For a clear presentation of the membrane developments, these are summarized according to the most important structural feature (C-F, ether-ketones, ether-sulfones, fluorenyles, phenylenes, benzimidazoles, phthalazinone-ether and imides) of the monomer (Table 4).
Table 4

Polymers for the preparation of VRFB membranes.

PolymerGroupStructure Examples
PFSA, PTFE, PVDF, ETFEfluoro-carbons-C-F
Poly (phenylene)hydro-carbon
Poly (ether ketone)hydro-carbon
Poly (ether sulfone)hydro-carbon
Poly (fluorenyl ether)hydro-carbon
Poly (phenylene ether)hydro-carbon
otherhydro-carbon-
Poly (benzimidazole)N-heterocycles
Poly (phthalazinone ether ketone)N-heterocycles
Poly (imide)N-heterocycles
Cation-exchange membranes (CEM), anion-exchange membranes (AEM) and amphoteric ion-exchange membranes (AIEM) are based on polymers with covalently bonded charges. AEM* and AIEM* are based on neutral polymers which build up a positive charge through interaction with hydronium-ions by lowering the pH value in their environment below pH 7.

4. Membrane Developments in Recent Years

The number of publications concerning membrane samples for VRFB has increased significantly since 2012. Polymer membranes can be subdivided with regard to elementary components of the polymer main chains. A distinction is made between fluorine-based polymers (fluoro-carbon) and fluorine-free (hydro-carbon) polymers. Nitrogen containing heterocycles-based polymers (N-heterocycles) are also used. For membranes composed of polymer mixtures, this subdivision refers to the polymer with the larger molar or mass fraction in the mixture. Polymers from these three groups are used in the development of polymer membranes for VRFB. In order to optimize the performance or the costs of a VRFB cell, suitable methods are selected to make chemical modifications to the polymers or to generate desired spatial structures. These chemical modifications can be applied to commercially available films (Figure 4a, MS107), commercial polymers (Figure 4b, MS151), or proprietary polymer syntheses (Figure 4b, MS143). The chemical methods aim to generate acidic, basic or amphoteric polymers whose chemical function influences the internal resistance of the VRFB and the cross-over between the half cells. As shown in Figure 3, synthetic membranes with distinctive structures can be used in VRFB cells.
Figure 4

The energy efficiency of VRFB cells at current densities < 100 mA cm−2 using: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

The developed and published membrane samples of the past years show these different structures and were tested in VRFB. An exception is the dense hydrophobic membrane, which can be used as a separation medium for gases but would act as an insulator in a VRFB. Dense homogeneous membranes are composed of fluoro-carbons (e.g., PFSA, ETFE-g-X, PVDF-g-X, sFPAE), hydro-carbons (e.g., QDAPP, sPEEK, sPSU) and N-heterocycles (PBI, sPI). Dense heterogeneous membranes represent a very frequently used membrane type, because it is relatively easy to influence their properties such as porosity (Figure 5b, MS189) by adding disperse components. Dense heterogeneous membranes can be found in fluoro-carbon, hydro-carbon and N-heterocycle-based membranes.
Figure 5

The energy efficiency of VRFB cells by using the developed membrane sample at current densities ≥ 100 mA cm−2 in recent years: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

Porous membranes can either have hydrophilic or hydrophobic character. Symmetrically porous (Figure 4c, MS266, hydrophilic) and asymmetrically porous (Figure 4a, MS98, hydrophobic) membranes get prepared and tested in scientific workgroups. Furthermore, multi-layer membranes are constructed to achieve certain properties, such as improved chemical stability (Table 7, MS167), lower costs (Figure 4b, MS147) or lower cross-over (Figure 4a, MS95). Figure 4 and Figure 5 show the observed energy efficiency of VRFB cells using the developed membrane samples and the publication year. Figure 4 shows results obtained with current densities less than 100 mA cm−2 and Figure 5 shows results obtained with current densities greater than 100 mA cm−2. The figures provide an overall picture of the achievable energy efficiencies of VRFB with different flow-battery targeted membranes. When comparing the results of the commercial membranes in Figure 2b with the results in Figure 4, it can be observed that VRFB with new membrane developments often achieve higher energy efficiencies than VRFB with each reference membranes. A direct comparison of membranes is only possible in the same cell and under identical experimental conditions. The comparison can be expressed in numerical terms by comparing the energy efficiencies achieved according to Equation (1). A value less than 1 is obtained if the energy efficiency of the VRFB using flow-battery targeted membranes is less than the energy efficiency of the VRFB with a reference membrane. EEr (energy efficiency ratio) is larger than one if the energy efficiency of the VRFB using flow-battery targeted membranes is higher. It should be mentioned that modifications to the cell other than the membrane further influence individual EE and thus the resulting ratio EEr. EE1 is the energy efficiency of the VRFB cell using flow-battery targeted membranes and EE2 the energy efficiency of the VRFB cell using a reference membrane. These energy efficiency ratios as well as the reference membranes are also given in Table 5, Table 6, Table 7, Table 8, Table 9, Table 10, Table 11, Table 12, Table 13 and Table 14.
Table 5

List of fluoro-carbon membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
91PTFE/Nafion/P/NdheCEM450.69-24.94.62 × 10−80.7809680761.070N212[53]
92PTFE/P/N/S-7dheCEM25--65.59 × 10−80.45809487821.155P/N[115]
93PTFE/SiO2sym----48--509386800.930N115[91]
94PTFE/SPEEK/SP60dheCEM---36--809390841.021N115[88]
95PTFE/ZrPdheCEM501.45--3.66 × 10−70.275409965640.901N115[86]
96PTFE/SE3/PdheCEM70--29.87.1 × 10−70.1781009979781.147N117[116]
97PVDF/M7sym-115-----120947975--[117]
98PVDF/M-23-125asym-125---7.9 × 10−70.66480958379--[118]
99PVDF/M2asym-105-----809487821.012N115[119]
100PVDF-g-St-co-/AIEMdhoAIEM581--1.18 × 10−70.153-----N117[120]
101PVDF g/AIEMdhoAIEM251.2-486.9 × 10−80.087-----N117[121]
102PVDF-g-PSSA/22dhoCEM1151.2-26.42.53 × 10−70.084609178731.082N117[68]
103PVDF-g-PSSA-co-PMAcdhoAIEM701.63--7.3 × 10−,0.089 N117[122]
104PVDF-g-St-co-./AIEMdhoAIEM250.80.7366.7 × 10−80.084-----N117[123]
105PVDF/SiO2-SO3H_42dheCEM30--52.11.12 × 10−70.1086090.383.575.60.967N115[124]
106PVDF/HA-45dhoCEM-2.67-462.5 × 10−7-1009584801.08N117[125]
107ETFE-g-PSSA-c- AIEM-IIdhoAIEM451.061.2436.12.9 × 10−90.004409679751.034N117[126]
108ETFE-g-PSSAdhoCEM380.88-14.73.9 × 10−80.057-----N117[126]
109ETFE-g-GMA- DG225dhoCEM502.4-181--1008773641.067N117[56]
110ETFE-g-PDMAEMA/40%dhoAEM70-1.7203.6 × 10−80.042-----N117[127]
111ETFE-g-poly(VP)dhoAIEM250.7----1209873711.044N117[128]
112ETFE-VB-DABACOdhoAEM50-1.5538-------N115[129]
113ETFE-VB-DMAdhoAEM50-1.338.8-------N115[129]
114ETFE-VB-TMAdhoAEM50-1.6438-------N115[129]
115PFSA AATMSdheAIEM*125-- 8.5 × 10−70.218809688831.051N115[71]
116PFSA AATMS (a-SiO2)dheAIEM*1881.05-35.12.32 × 10−70.268809172691.062N117[64]
117PFSA CC (CCM)dheCEM------1209586811.056N115[130]
118PFSA FC (N/FC-5)dheCEM-0.925-314.1 × 10−80.5809578741.250N117[112]
119PFSA GO (GO-0.01)dheCEM27.750.96-22.41--809286791.068N117[51]
120PFSA ND (AMH-3)dheCEM183---8.64 × 10−70.281409785820.965N117[47]
121PFSA Ormosil (N/O)dheCEM2170.97-23.61.85 × 10−70.050809684811.210N117[131]
122PFSA [PDDA PSS]5dheAIEM----2.85 × 10−70.095809873721.091N117[85]
123PFSA [PDDA ZrP]3dheAIEM---8--509585811.052N115[132]
124PFSA PEI (N/P2.5)dheAIEM*1960.89 5.23 × 10−7 5096.288.485.11.001N117[67]
125PFSA PVDF (N/P0.2)dheCEM1000.64-16.2--809488841.037D-520[133]
126PFSA (N-sDDS)dheCEM1930.92-14.3--709685811.177N117[134]
127PFSA (N/Si/Ti)dheCEM2250.95-22.54.3 × 10−7-309582781.012N117[76]
128PFSA (N-SiO2)dheCEM178---8.64 × 10−7-509391841.000N117[135]
129PFSA SPEEK (N/S)dheCEM1001.67--1.93 × 10−70.053509885830.980N117[136]
130PFSA (N-TiO2)dheCEM900.85-19.136.72 × 10−60.297608981721.027N117[77]
131PFSA (CS/PWA)dheAIEM*58-----608293761.070N212[44]
132PFSA (ZrNT)dheCEM1550.927--3.6 × 10−90.010409881791.090N117[137]
133SFPAE 1.8_45dhoCEM451.8----80998382--[113]
134SFPAE 1.8dhoCEM601.8-481.16 × 10−80.2191009892901.047N212[39]
135SFPAE (PVDF-co-/10%)dheCEM601.6-35--1009988880.999SFPAE[138]
Table 6

List of poly(phenylene)-based hydro-carbon membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
136PP/SDAPP1.8dhoCEM411.8----2009688851.181N117[139]
137PP/SDAPP2.2dhoCEM502.2----2004888420.583N117[139]
138PP/QDAPP0.8dhoAEM54-0.8---2009688851.181N117[139]
139PP/QDAPP1.2dhoAEM54-1.2---2009688851.181N117[139]
140PP/AMPP11dhoAEM80-1.131.63.3 × 10−90.034409957570.912N117[140]
141PP/AMPP15dhoAEM80-1.545.23.2 × 10−80.330409859580.920N117[140]
142PP/QDAPP2dhoAEM--0.8771.4 × 10−60.6662009790871.094N212[52]
143PP/SDAPP (Sample1)dhoCEM-1.4-364.4 × 10−70.094509990891.011N117[43]
144PP/p-TPN1dhoAEM35-2.15187.4 × 10−80.0188010085851.06N212[141]
Table 7

List of ether-ketone-based hydro-carbon membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
145SPEEK/DS92dhoCEM652.35-883.06 × 10−60.2432009382771.048N212[55]
146SPEEKdhoCEM1001.8--2.43 × 10−70.067509787850.998N117[136]
147SPEEK (N/S)dheCEM1001.67--1.93 × 10−70.053509885830.980N117[136]
148SDPEEK (SD4-6-100)dhoCEM1001.2-42.50.38 × 10−70.027509890881.046N115[101]
149SDPEEK (C-SD5-5-50)dhoCEM501.65-29.80.48 × 10−70.034509793901.024N115[101]
150SPEEKdhoCEM351.5-276.88 × 10−70.433409891891.145N112[33]
151SPEEK (PANI 80/20)dheCEM371.44-212.67 × 10−70.168409893911.175N112[33]
152SPEEKdhoCEM128--60.61.61 × 10−60.797409395881.060N115[142]
153SPEEK (SPEEK/RP)dheCEM108--51.86.9 × 10−70.3421209881801.060N115[142]
154SPEEK-co-PEEKdhoCEM652.12-551.84 × 10−60.571809388821.062N117[58]
155SPEEK (S/SBA-20)dheCEM611.72-31.86.2 × 10−70.193809789861.121N117[58]
156SPEEKdhoCEM752.25-863.06 × 10−60.8122009672701.094N117[60]
157SPEEK (SPEEK-15%)dhoCEM751.9-621.9 × 10−60.4962009872721.125N117[60]
158SPEEK/DS 57.99dhoCEM1951.58-30.572.42 × 10−80.008-----N117[143]
159SPEEK/DS 86.49dhoCEM1952.35-83.022.28 × 10−60.740-----N117[143]
160SPEEKdhoCEM801.75-32.64.2 × 10−60.636609084761.133N117[72]
161SPEEK (g-C3N4-1.5)dheCEM800.86-20.74 × 10−70.061609885841.200N117[72]
162SPEEKdhoCEM70---1.04 × 10−70.2992009773711.118N117[82]
163SPEEK (PDA-0.5h)dhoCEM70---1.67 × 10−70.0482009968671.055N117[82]
164SPEEK/S67-DMFdhoCEM551.97-382 × 10−70.0531209783811.095N117[84]
165SPEEK/S87-DMFdhoCEM552.43-813.5 × 10−60.9211209483771.041N117[84]
166SPEEKdhoCEM70-----20010065651.016N115[144]
167PTFE/SPEEK/PTFEdheCEM130-----80998685-N115[144]
168SPEEKdhoCEM2002-501.14 × 10−60.877-----N117[105]
169SPEEK/PVDF/TPAdheCEM2001.9-35.35.17 × 10−70.398209387811.041N117[105]
170SPEEKdhoCEM652.24-62.69 × 10−70.2812009861600.952N117[92]
171SPEEK (S/A 5%)dheCEM651.99-53.52 × 10−70.0632009770681.079N117[92]
172SPEEK (S/S 5%)dheCEM581.92-52.72 × 10−70.0632009873721.143N117[92]
173SPEEK (S/T 5%)dheCEM682.07-60.63.5 × 10−70.1092009968671.063N117[92]
174C-SPEEK-50dheCEM901.34-50--809887851.040N115[59]
175SPEEKdhoCEM802.16-30.91.56 × 10−60.467------N117[145]
176SPEEK (S/G)dheCEM901.98-49.48.7 × 10−70.261809886841.063N117[145]
177SPEEKdhoCEM991.49-26.71.56 × 10−60.427-----N117[146]
178SPEEK (S/OCN-1)dheCEM1001.56-48.29.09 × 10−70.249609886841.000N117[146]
179SPEEKdhoCEM521.85-37.11.15 × 10−60.3302009868671.047N117[38]
180SPEEK (S/GO 3)dheCEM502.07-44.95.9 × 10−70.1712009872711.109N117[38]
181SPEEK (S/P-0)dhoCEM-1.79-38.41.12 × 10−71.172509091821.007N117[66]
182SPEEK (S/P-3/PEI)dheCEM-1.38-32.94.78 × 10−80.073509789871.065N117[50]
183SPEEKdhoCEM-2.03-434.2 × 10−60.627309680771.100N117[147]
184SPEEK (PPD-GO-1)dheCEM-1.08-221.2 × 10−60.179309786831.179N117[147]
185SPEEKdhoCEM792.1-47.32.5 × 10−70.104809776741.021N117[40]
186SPEEK (S/P 15)dheCEM741.79-39.61 × 10−70.042609883811.069N117[40]
187SPEEKdhoCEM80---4.03 × 10−70.490-----N212[148]
188SPEEK/SCCTdheCEM90---3.22 × 10−70.391509986851.104N212[148]
189SPEEK (TiO2 5%)dheCEM-1.5-232.45 × 10−70.07650988280.41.084N117[149]
190SPEEK (SPEEK-40)dhoCEM901.45--0.36 × 10−70.045509989881.033N115[83]
191SPEEK (TPA/PP)dheCEM240---4.78 × 10−70.58135.79686831.014N212[150]
192SPEEK (S/PAN 20)dhoCEM751.78-5811.3 × 10−70.300809687841.065N117[151]
193SPEEK (PSP)dhoCEM750.74-7.81.37 × 10−80.050209976750.935N117[152]
194PEEK-QADMPEK 3dhoAEM43-1.7518.87.64 × 10−70.244809985841.050N117[98]
195QPEK-C-TMAdhoAEM40-1.4368.2 × 10−90.02830998382-N212[153]
196SPEKS/sGO 0.5dheCEM-0.76-315 × 10−80.161409983.382.51.12N212[154]
197SPEEK/ZC-GO-2dheAIEM751.87-36.512.7 × 10−70.1895098.592.391.41.09N117[155]
198S/TPAM-1%dhoAIEM1081.55-39.33.04 × 10−70.0746097.586.683.81,018N115[156]
199SPEEK/L15dhoCEM811.11-29.621.7 × 10−80.08612099.583.983.5-N212[157]
200CrSPK45-SdhoCEM-1.67-22.166.1 × 10−90.12809886.7851.08N117[158]
201Q2-ADMPEK-4dhoAEM--2.0724,05--809988.587.61.09N212[159]
202CQSPK-6dhoAEIM 0.95-21.61.05 × 10−90.0646098.482.781.41.07N117[160]
203SPAEK/Ce2Zr2O7 2%dheCEM-1.31-521.29 × 10−90.0374099.982.682.11.087N212[161]
Table 8

List of PSU, PPSU and PES-based hydro-carbon membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
204PSU/PVDF/imi sIPNdheAEM---21--80998584--[162]
205PSU/CMPSF 72symAEM45-1.51---809987861.048N115[102]
206PSU/ImPSf/SPEEKdheAIEM652.04-561.5 × 10−80.0712009879771.069N212[55]
207PSU/PVP 50dheAIEM50-----1009979781.026N212[163]
208PSU/PVP/PS M90asymAIEM130-----80908778--[164]
209PSU/CPSF-PysymAEM88-----1009789861.051N115[165]
210PSU/TMAdhoAEM43---2.6 × 10−8-309688851.012N212[166]
211PSU/PSf-c-PTA-1.4dhoAEM--1.736.72.57 × 10−70.19812098.485.784.31.12N115[167]
212PSU/SPSF-62dhoCEM761.26-24.52.94 × 10−60.43810098.887.286.21.14N117[168]
213PSU/SPSF/g-C3N4-1dheAIEM851.11-19.97 × 10−7-1009889.187.31.15N117[169]
214PPSU/CMP-2dhoAEM42.5-1.9535.31.5 × 10−80.005809786831.049N117[96]
215PPSU/QA-1.7dhoAEM57.5-1.716--8010075701.106N212[114]
216PPSU/AEMdhoAEM50-----601007070-N212[170]
217PPSU/S-needledhoCEM1151.95--2.07 × 10−70.161509885841.005N117[48]
218PPSU/BPSH35dhoCEM-1.52-401.6 × 10−90.123809976751.042N212[49]
219PPSU/S2B2dhoAIEM*501.2-40.2 1009979771.305N117[34]
220PES/PVP M3asymAEM115---4 × 10−6-80938579--[171]
221PES/SPEEK M-35-13symCEM85-----80918678--[172]
222PES/SPEEK M-35-6asymCEM160-----80928578--[173]
223PES/SPEEK M3dheCEM65-----809987861.049N115[99]
224PES/SPEEK/FT 10%asymCEM180---3.98 × 10−6-80958682-N115[174]
225PES/SPEEK/N 2.56asymCEM------809987861.012N115[81]
226PES/SPEEK/PDDA 7.5symAIEM132-----809892901.071N115[175]
227PES/SPEEK/PPyasymAIEM*120-----809791881.073N115[95]
228PES/SPEEK/SiO2 M2dheCEM125--25--808287940.989N115[93]
229PES/SPEEK/ZSM-35asymCEM------809893911.109N115[97]
230SPES/SPEEKdheCEM700.7-21.6--509886851.090N212[176]
231SPESdhoCEM-2.07-121.932.5 × 10−60.809------[143]
232SPAES S/NdheCEM------2009975741.035N115[69]
233SPES (IL-30)asymCEM----1.41 × 10−8-1409980.1379.30.98N212[177]
234MD2.0-10dheAEIM----1.7 × 10−70.1348099.382.6821.025N115[178]
Table 9

List of fluorenyl-ether-based hydro-carbon membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
235QA-PFEdhoAEM56-2.0---6010070701.0N212[37]
236SPECIALdhoCEM112.51.92-29-0.255066.273.748.8-N117[179]
237F-SPFEKdhoCEM112.51.88-33-0.755076.180.361.1-N117[179]
238F-SPFEK-APTESdhoCEM112.51.75-26-0.505080.479.764.1-N117[179]
239SPECIALdhoCEM1611.92-39-0.216087.5---N117[180]
240SPFEK/3%SIO2dheCEM1551.83-36.6-0.296087.5---N117[180]
241SPECIALdhoCEM1801.92-27.89.85 × 10−70.404080.364.651.9-N117[180]
242SPECIALdhoCEM-1.87---------N117[181]
243SPFEK/5ZrPSPPdheCEM-1.96----508960.754-N117[181]
244SPFEK-[PDDA/PSS]n2dheAIEM130----------N117[182]
245SPFEK 20.7 [PDA/PSS]2symAIEM151---5.92 × 10−70.36-----N115[183]
246SPECIALdhoCEM1601.57-36.52.67 × 10−70.13-----N115[184]
247SPFEKA 10%.dhoAIEM1601.52-30.61.56 × 10−70.08-----N115[184]
248SPFEKA-20%dhoAIEM1601.47-30.90.88 × 10−70.04-----N115[184]
249HSPAEKdhoCEM601.72-38.55.5 × 10−70.16809885831.05N117[90]
Table 10

List of poly(phenylene ether)-based hydro-carbon membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
250BrPPO/Py-42dhoAEM50--130.12 × 10−70.0210098.184820.932N212[35]
251BrPPO/Py-56dhoAEM50--180.2 × 10−70.0310097.794921.045N212[35]
252BrPPO/Py-70dhoAEM50--210.36 × 10−70.0510096.790870.989N212[35]
253SPPO-GOdheCEM-1.17-16.31.1 × 10−80.0540987169.6-N212[185]
Table 11

List of other hydro-carbon-based membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
254QPTMdhoAEM89-2.088.81.19 × 10−70.0345010075751.033N117[41]
255QVTD 2-3dhoAEM------40958075--[186]
256VBC AVSH-3dhoAEM------40957575--[187]
257PVC/silicasym-390-----408988780.907N115[188]
258Si-PWA/PVAdheCEM1251.2--6.9 × 10−80.119-----N115[189]
259DHIM-375dhoCEM1000.69-311.56 × 10−70.05220918072-N117[190]
260ZPPT-6dhoAIEM80-1.2230--509880781.05N117[57]
261PIM-1asym-“0.75”-----2097.192.589.91.2N112-[191]
Table 12

List of PBI-based N-heterocycle membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
262mPBIdhoAEM27---2.86 × 10−90.0085099.580.4800.941N115[65]
263BlpPBIdhoAEM27---3.45 × 10−80.099509988.487.51.029N115[65]
264mPBI-15dhoAEM15---0-12099.86867.90.893N212[192]
265mPBI-35dhoAEM35---0-120995352.50.691N212[192]
266p-PBIsymAEM87---4.5 × 10−80.028409988871.145N112[193]
267PBI-0%dhoAEM16-----409550470.595N117[70]
268PBI 10%.symAEM45---1.17 × 10−7-409979780.987N117[70]
269PBI-200asymAEM100---3 × 10−9-809983821.206N211[194]
270PBI-O/PBI-34symAEM34-----809991901.092N115[195]
271CSOPBI-NH2 (9/1)dhoAIEM*550.24-47.46 × 10−90.001609886841.024N117[87]
272-6F-co-10%BIdhoAIEM*641.56--2.24 × 10−11-309991901.027N117[63]
273-6F-co-10%BI-clddhoAIEM*651.50--1.28 × 10−11-309990891.018N117[63]
274FPAE-6F-PBI S1B1dheAIEM*501.02-23.8--10010064641.085N117[34]
275B20N10dhoAEIM30--23.61.95 × 10−90.0068010082.282.21.068N115[196]
276CPBI-70-NMGdhoAEM------120998685.31.036N212[197]
2770,7µm PBIasymAEM30-----12098.585831.034N212[198]
278PWN/F6PBI(9/1)dhoAIEM451.51----409981811N212[199]
279PVDF-PBIasymAEM------6098.483.3821.03N117[200]
280sPBIdhoAEIM220.2--58.15.74 × 10−7-242938681-N212[201]
281PE/PBIdheAEM25--20.95.04 × 10−70.346200998180.111.03N212[202]
Table 13

List of poly(phthalazinone ether)-based N-heterocycle membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
282PyPPEK-2dhoAEM--1.417.4--609985841.000N117[203]
283QAPPEK-2dhoAEM--1.521--609983820.964N117[203]
284QAPPEKKdhoAEM--1.56---409989881.026N117[103]
285PyPPEKK-4dhoAEM42-1.5516.5--409890891.034N117[103]
286QBPPEK 80dhoAEM47-1.5323.8--409989881.023N117[204]
287QAPPEKK-4dhoAEM50-1.5620.8--20989391.31.016N117[100]
288SPECdhoCEM2001.272-32.342.77 × 10−70.024609969680.919N117[80]
289SPPEK TPA-17dheCEM2001.142-33.285.75 × 10−70.049609976751.010N117[80]
290SPPEK/WO3dheCEM210--48.153.97 × 10−70.034509880791.032N117[79]
291SPPEK P-90dhoCEM531.51-23.2--409889871.023N115[61]
292SPPES/SP-02dhoCEM2601.42-17.421.24 × 10−70.055409373681.004N117[205]
Table 14

List of poly(phthalazinone ether)-based N-heterocycle membrane samples.

NoMembrane SampleMembraneMembrane PropertiesVRFB PropertiesReference
MSPolymer/Sample NameStrucChemdIECCIECAWUDCDrCDCEVEEEEErMemPub
µmmmol g−1mmol g−1wt.%cm2 min−1%mA cm−2%%%
293SPI (ODA)dhoCEM601.2-21.932.17 × 10−70.127-----N117[74]
294bSPI (APABI)dhoAIEM*541.3-28.801.75 × 10−70.102-----N117[74]
295bSPI(MDA)dhoCEM551.37-34.884.43 × 10−70.259-----N117[74]
296bSPI(BAPP)dhoCEM571.14-20.032.89 × 10−70.1691209964631.018N117[74]
297SPI(H)dhoCEM501.65----50957470--[206]
298s-FSPIdhoCEM-1.50-17.787.4 × 10−80.0556010077771.160N115[207]
2996F-SPI-50dhoCEM----2.27 × 10−70.1726099.572.4721.091N115[75]
300SPIdhoCEM501.58-25.72.25 × 10−70.165609878761.086N115[78]
3016F-s-bSPIdhoCEM351.54-16.51.18 × 10−70.0876010079791.129N115[78]
302SPIdhoCEM691.75-39.921.89 × 10−70.111709370650.956N117[104]
303SPI/AlOOH-10dheCEM580.95-48.591.14 × 10−70.067709673701.029N117[104]
304SPI(APABI)dhoAIEM*651.24-22.797.2 × 10−80.0423010077771.069N117[208]
305SPI(BAPP)dhoCEM621.49-27.084.8 × 10−80.0283010079791.097N117[208]
306SPI(MDA)dhoCEM641.48-26.942.36 × 10−70.138309872710.986N117[208]
307SPIdhoCEM451.61-41.401.89 × 10−70.123409492870.998N117[94]
308SPI/CSdheAIEM*501.65-28.661.12 × 10−70.073409891891.020N117[94]
309SPIdhoCEM651.58-37.142.37 × 10−70.139-----N117[209]
310SPI/MoS2dheCEM651.25-29.362.02 × 10−70.119809565621.016N117[209]
311SPI/s-MoS2dheCEM661.70-32.201.23 × 10−70.072809666631.033N117[209]
312SPIdhoCEM501.25-54.72.6 × 10−60.388408977691.045N117[210]
313SPI/PEI-GO-2dheAIEM*501.16-44.27 × 10−70.104409582771.167N117[210]
314SPIdhoCEM551.40-38.461.9 × 10−70.111-----N117[54]
315SPI/TiO2dheCEM491.24-32.942.02 × 10−70.118709772691.022N117[54]
316SPIdhoCEM501.25-54.72.6 × 10−60.388809465631.050N117[211]
317SPI/ZGO-4dheAIEM*501.52-63.11.2 × 10−60.179409383771.132N117[211]
318SPIdhoCEM661.51-37.522.37 × 10−70.139709371661.048N117[212]
319SPI/ZrO2-15dheCEM740.93-53.192.18 × 10−70.127709770681.079N117[212]
320SPIdhoCEM1500.40----1009873721.220N117[213]
While energy efficiency describes the performance of a VRFB by charge and discharge cycles, membrane characteristics are usually influenced by a number of parameters. The frequently investigated membrane properties which can influence VRFB performance are the membrane thickness, water uptake, ion-exchange capacity, electrical resistance and the diffusion coefficient for vanadyl-cations. Furthermore, the ion-selectivity [112] is an important quality. Equation (2), like Equation (1), calculates a ratio for comparison to the reference membrane. Dc1 is the diffusion coefficient (VO2+) of the membrane samples and Dc2 the diffusion coefficient (VO2+) of the reference membranes. Table 5, Table 6, Table 7, Table 8, Table 9, Table 10, Table 11, Table 12, Table 13 and Table 14 list the best membrane sample selected from each publication. The tables contain information about the specific membrane sample as well as VRFB performance data. In addition to the sample name from the respective publication, the starting polymer, the structure and the chemical character (AEM, CEM or AIEM) are also listed.

4.1. Membrane Properties

Membrane samples are produced by chemical modification of commercially available membranes and films or by coating and subsequent phase inversion (solvent evaporation or precipitation). The thickness of the membrane samples depicted in Figure 6 is the result from these processes and also of possibly occurring membrane swelling in battery electrolyte.
Figure 6

The thickness of developed membranes in recent years: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

Generally, the thickness of the membrane defines the distance between the electrodes. For a low electric resistance of an electrochemical cell, the smallest distance between the electrodes is desirable. The fluoro-carbon-based membranes (Figure 6a) have thicknesses from 25 µm to 225 µm, the hydro-carbon-based membranes in Figure 6b thicknesses from 35 µm to 390 µm and the N-heterocycle-based membranes in Figure 6c thicknesses from 15 µm to 260 µm. The PFSA membranes MS116, MS120, MS121, MS124, MS126, MS127 and MS128 are modified Nafion (N117) membranes with an original thickness of about 180 µm. ETFE membranes modified by grafting (MS107-MS114) use commercially available ETFE films (25 or 50 µm). A commercial film is also used for the pore-filled PTFE membrane (MS92). The non-ionic PVDF membranes MS97, MS98 and MS99 have porous structures. The hydrophobic and asymmetrically porous MS98 has a separation layer in the submicron range with pore sizes of about 50 nm. The hydrophilic asymmetrically porous MS99 has a similar structure. Further asymmetric membranes can be found in the group of hydro-carbon-based polymer membranes. These include MS208 with an average pore size of 1.78 nm, MS225 (asymmetrically composed) with a Nafion separating layer of approximately 1 µm and MS229 (asymmetrically composed) modified by a zeolite layer with pore sizes of 0.3–1 nm. In addition to an asymmetrically porous membrane, MS269 with a separating layer of about 5 µm, symmetrically porous PBI-based membranes with thicknesses between 34 µm (MS270) and 87 µm (MS266) were developed. The thickness of a membrane defines the distance between the electrodes in the VRFB and directly influences the material cost. Furthermore, separation effect increases with the thickness of the membrane up to a critical pore size. The simultaneous reactions on the anode and cathode surfaces during charging and discharging require the exchange of protons. Sulfuric acid, the solvent of the reactive vanadium species, as well as sulfonated polymers are excellent proton conductors. The ion exchange capacity of a membrane describes the acid concentration of the polymer membrane. The ion-exchange capacities (IECc, cations) indicated for PFSA membranes are between 0.85 and 1.67 mmol g−1, whereby MS129 containing sulfonated PEEK in addition to Nafion enables the highest IECc. The FPAE membranes have an IECc of 1.6 to 1.8 mmol g−1. For the DAPP membranes in Figure 7b the IECc is between 1.4 and 1.8 mmol g−1 and for the PEEK membranes between 0.74 (MS193) and 2.43 mmol g−1 (MS165). MS206 has an IECc of 2.04 mmol g−1, MS217 to MS219 an IECc of 1.2 to 1.95 mmol g−1, MS230 an IECc of 0.7 mmol g−1 and MS231 an IECc of 2.07 mmol g−1. The PF-based membranes have an IECc of 1.47 mmol g−1 to 1.96 mmol g−1. For MS259 and MS260 an IECc of 1.2 and 0.69 mmol g−1 was measured.
Figure 7

The ion-exchange capacity (IECc) of tested polymer membranes in recent years: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

The PBI membranes in Figure 7c have an IECc of 0.24 to 1.56 mmol g−1, the PPEK membranes an IECc of 1.14 to 1.51 mmol g−1 and the PI membranes an IECc of 0.4 to 1.75 mmol g−1. In the development of membranes, IECc between 1 and 2 mmol g−1 is predominantly achieved. The PFSA membranes in the fluoro-carbon group increasingly exhibit IECc smaller than 1 mmol g−1. In the group of hydro-carbon-based membranes, especially when using PEEK, IECc of more than 2 mmol g−1 can be reached. Figure 8 shows the diffusion coefficients for vanadyl cations of membrane samples that have been tested and published for use in VRFB since 2005. Low diffusion coefficients lead to low vanadium cross-over during charging and discharging of the battery and therefore influences the coulombic efficiency. Diffusion coefficients (VO2+) from 2.9 × 10−9 to 6.72 × 10−6 cm2 min−1 for fluoro-carbon-based membranes and 1.6 × 10−9 to 4.2 × 10−6 cm2 min−1 for hydro-carbons, as well as 1.28 × 10−11 to 2.6 × 10−6 cm2 min−1 for N-heterocycles, have been published. Selected diffusion coefficients ranges:
Figure 8

Measured diffusion coefficients of tested polymer membranes in recent years: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

PTFE 4.62 × 10−8 to 7.1 × 10−7 cm2 min−1 PVDF 6.7 × 10−8 to 7.9 × 10−7 cm2 min−1 ETFE 2.9 × 10−9 to 3.9 × 10−8 cm2 min−1 PFSA 3.6 × 10−9 to 6.72 × 10−6 cm2 min−1 FPAE (MS134) 1.16 × 10−8 cm2 min−1 PPh 3.3 × 10−9 to 1.4 × 10−6 cm2 min−1 PEEK 1.05 × 10−9 to 4.2 × 10−6 cm2 min−1 PSU 1.5 × 10−8 to 2.94 × 10−6 cm2 min−1 PPSU 1.6 × 10−9 to 2.07 × 10−7 cm2 min−1 PES 1.41 × 10−8 to 4 × 10−6 cm2 min−1 PF 8.8 × 10−8 to 9.85 × 10−7 cm2 min−1 PPE 1.1 × 10−8 to 3.6 × 10−8 cm2 min−1 Other 6.9 × 10−8 to 1.56 × 10−7 cm2 min−1 PBI 1.28 × 10−11 to 5.74 × 10−7 cm2 min−1 PPEK 1.24 × 10−7 to 5.75 × 10−7 cm2 min−1 PI 4.8 × 10−8 to 2.6 × 10−6 cm2 min−1. The results on membrane thickness, ion-exchange capacity and vanadyl permeation summarized in Figure 6, Figure 7 and Figure 8, as well as the Supplementary data showing water uptake and anion-exchange capacity of membrane samples, are the most frequently investigated characteristics in publications on membrane development for VRFB cells. Other important properties are electrical resistance and ion-selectivity, for which the goal is to achieve a high proton conductivity, combined with the lowest vanadium-ion permeability possible. It is described in [113] that membrane thickness in particular has an influence on this and can be optimized accordingly. With increasing ion-exchange capacity, water uptake increases in non-crosslinked membranes [84,114]. Due to the large number of data points, not every point in Figure 6, Figure 7 and Figure 8 is marked with the sample number from the following Table 5, Table 6, Table 7, Table 8, Table 9, Table 10, Table 11, Table 12, Table 13 and Table 14. The results pertaining water uptake, Dr as well as the ion-exchange capacity (IECA) for AEM and AIEM are presented as Supplementary Materials. The Table 5, Table 6, Table 7, Table 8, Table 9, Table 10, Table 11, Table 12, Table 13 and Table 14 list the membrane samples according to their membrane polymer structures, e.g., poly(sulfones). The tables start with the fluoro-carbon-based membranes followed by the hydro-carbon and the N-heterocycle-based membranes.

4.2. Membrane Impact on VRFB Cell Performance

A VRFB cell is built up with frames, electrode felts, bipolar plates, electrolyte and membranes. Figure 9, Figure 10, Figure 11, Figure 12, Figure 13 and Figure 14 show the efficiencies of VRFB cells at different current densities. These cells are equipped with membranes from Table 5, Table 6, Table 7, Table 8, Table 9, Table 10, Table 11, Table 12, Table 13 and Table 14.
Figure 9

The energy efficiency of VRFB cells by using membrane samples at current densities < 100 mA cm−2: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

Figure 10

The voltage efficiency of VRFB cells by using membrane samples at current densities < 100 mA cm−2: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

Figure 11

The energy efficiency of VRFB cells by using membrane samples at current densities < 100 mA cm−2: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

Figure 12

The coulombic efficiency of VRFB cells by using membrane samples at current densities ≥ 100 mA cm−2: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

Figure 13

The voltage efficiency of VRFB cells by using membrane samples at current densities ≥ 100 mA cm−2: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

Figure 14

The energy efficiency of VRFB cells by using membrane samples at current densities ≥ 100 mA cm−2: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

Figure 9 shows the coulombic efficiencies (CEL) of VRFB cells with current densities of less than 100 mA cm−2, constructed with either fluoro-carbon, hydro-carbon or N-heterocycle-based samples. CEL ranging from 65% to 99% were achieved with fluoro-carbon-based membrane samples, CEL from 66% to 100% with hydro-carbon-based membranes and CEL from 82% to 100% with N-heterocycle-based membranes. In fluoro-carbons (Figure 9a), VRFB cells using MS95 (PTFE, dhe, CEM), MS133 (FPAE, dho, CEM), MS134 (FPAE, dho, CEM), MS132 (PFSA, dhe, CEM), MS129 (PFSA, dhe, CEM), MS126 (PFSA, dhe, CEM), MS122 (PFSA, dhe, AIEM) and MS107 (ETFE, dho, AIEM) achieve high CEL of at least 98%. In hydro-carbon-based membranes VRFB cells with modified PEEK membranes MS195 (PEEK, dho, AEM), MS161 (PEEK, dhe, CEM) and MS178 (PEEK, dhe, CEM) also achieve high CEL of at least 98%. Furthermore, MS235 (PF, dho, AEM), MS254 (other, dho, AEM), MS195 (PSU, dho, AEM), MS218 (PPSU, dho, CEM), MS205 (PSU, sym, AEM) and MS225 (PES, asym, CEM) achieve similarly high CEL. In Figure 9c VRFB cells with PBI membranes MS263 (PBI, dho, AEM*), MS264 (PBI, dho, AEM*), MS262 (PBI, dho, AEM*), MS272 (PBI, dho, AEM*), MS269 (PBI, asym, AEM*) and MS270 (PBI, sym, AEM*) show CEL of at least 98% as well. The VRFB cells with PPEK-based membranes (MS282-MS291) all show a CEL of at least 98% except for MS292 (PPEK, dho, CEM). VRFB cells equipped with PI membranes MS298 (PI, dho, CEM), MS301 (PI, dho, CEM), MS304 (PI, dho, AIEM*), MS305 (PI, dho, CEM) and MS308 (PI, dhe, AIEM*) all reach high CEL of at least 98%. In some cases, the CEL depend on the membrane thickness. This is observed with the PTFE-based membranes (Figure 9a). The CEL ranges from 94% (MS92/25 µm) to 99% (MS96/70 µm). The VRFB equipped with MS91 (45 µm) shows a CEL of 96%. Other examples do not show this correlation, e.g., MS111 with a thickness of 25 µm and a CEL of 98% at 120 mA cm2. In summary, it appears to be possible to reach high CEL with membrane polymers from all three groups. Figure 10 shows the voltage efficiencies (VEL) of VRFB cells using the specified membrane samples with current densities less than 100 mA cm−2. The VEL are 66% to 97.5% with fluoro-carbon-based membranes, 60.7% to 95% with hydro-carbon-based membranes and 65% to 96.4% with N-heterocycle-based membranes. For the fluoro-carbon-based membranes in Figure 10a, at a current density of 80 mA cm−2, the highest VEL of VRFB cells are achieved using MS94 (PTFE, dhe, CEM), MS115 (PFSA, dhe, AIEM*), MS99 (PVDF, asym), MS119 (PFSA, dhe, CEM), MS98 (PVDF, asym), MS126 (PFSA, dhe, CEM) and MS91 (PTFE, dhe, CEM). The minimum VEL achieved here is 80%. For the hydro-carbon-based membranes in Figure 10b, at a current density of 80 mA cm−2, the highest VEL of VRFB cells are obtained using MS229 (PES, asym, CEM), MS226 (PES, sym, AIEM), MS227 (PES, asym, AIEM), MS155 (PEEK, dho, CEM), MS154 (PEEK, dho, CEM), MS174 (PEEK, dhe, CEM), MS192 (PEEK, dho, CEM), MS167 (PEEK, dhe, CEM), MS176 (PEEK, dhe, CEM), MS214 (PPSU, dho, AEM), MS208 (PSU, asym, AIEM), MS194 (PEEK, dho, AEM) and MS249 (PF, dho, CEM). The minimum VEL achieved here is 85%. For the N-heterocycle-based membranes in Figure 10c, at a current density of 80 mA cm−2, the highest VEL of VRFB cells are achieved using MS270 (PBI, sym, AEM*) and MS269 (PBI, asym, AEM*). All VEL measured here are above 80%. VEL of at least 95% are reached by VRFB cells at lower current densities with MS123 (PFSA, dhe, AIEM), MS121 (PFSA, dhe, CEM), MS115 (PFSA, dhe, AIEM*), MS119 (PFSA, dhe, CEM), MS134 (FPAE, dho, CEM), MS131 (PFSA, dhe, AIEM*), MS191 (PEEK, dhe, CEM), MS152 (PEEK, dho, CEM), MS310 (PI, dhe, CEM), MS270 (PBI, sym, AEM*), MS263 (PBI, dho, AEM*) and MS291 (PPEK, dho, CEM). Figure 10a,c show the tendency of decreasing VEL with increasing current density, which cannot be observed as a trend for hydro-carbon-based membranes. This can be explained by a lower electrical resistance, which can be achieved with aromatic polymers with high degrees of sulfonation. Figure 11 shows the energy efficiency (EEL) of VRFB cells using the specified membrane samples with current densities less than 100 mA cm−2. For VRFB cells with fluoro-carbon-based membrane samples, the EEL ranges from 63% to 95%. For hydro-carbon-based membranes the EEL ranges from 57% to 94% and for N-heterocycle-based membranes the EEL ranges from 63% to 94%. For VRFB cells with fluoro-carbon-based membranes, high EEL of at least 85% are measured with MS133 (FPAE, dho, CEM), MS134 (FPAE, dho, CEM), MS126 (PFSA, dhe, CEM), MS125 (PFSA, dhe, CEM), MS95 (PTFE, dhe, CEM) and MS124 (PFSA, dhe, AIEM*). For VRFB cells with hydro-carbon-based membranes, EEL of at least 90% are achieved with MS215 (PPSU, dho, AEM), MS235 (PF, dho, AEM), MS232 (FPAE, dhe, CEM), MS151 (PEEK, dhe, CEM), MS249 (PF, dho, CEM), MS149 (PEEK, dho, CEM) and MS228 (PES, dhe, CEM). With many other membranes from Figure 11b, EEL of at least 85% were achieved. In VRFB cells with N-heterocycle-based membranes, high EEL of at least 85% are measured with MS263 (PBI, dho, AEM*), MS286 (PPEK, dho, AEM), MS287 (PPEK, dho, AEM), MS291 (PPEK, dho, CEM), MS301 (PI, dho, CEM), MS299 (PI, dho, CEM), MS272 (PBI, dho, AIEM*), MS273 (PBI, dho, AIEM*), MS308 (PI, dhe, AIEM*), MS284 (PPEK, dho, AEM), MS266 (PBI, sym, AEM*), MS307 (PI, dho, CEM), MS263 (PBI, dho, AEM*) and MS270 (PBI, sym, AEM*). The improvement of the EEL e.g., at 80 mA cm−2 is caused by the optimization of different membrane properties. The series of SFPAE membranes (28, 45, 80 µm) in [114] showed a different energy efficiency due to different membrane thickness. A water uptake of 30% leads to the highest energy efficiency of 90% at 50 mA cm−2 by using PEEK-based CEM. It has been shown that with a range of different membrane samples, high EEL of over 90% at current densities of less than 100 mA cm−2 are feasible. These high efficiencies are achieved by cells with dense fluoro-carbon and dense hydro-carbon-based membranes as well as dense and symmetrically porous N-heterocycle-based membranes. The respective membranes are composed of different polymers and can be assigned to CEM, AEM, AEM* and AIEM*. Figure 12 shows the coulomb efficiencies (CEH) of VRFB cells with current densities of at least 100 mA cm−2 using the specified membrane samples. In the VRFB cells from Figure 12a equipped with the fluoro-carbon-based membrane samples, CEH of 87% to 99.5% were measured. The VRFB cells equipped with the hydro-carbon-based membranes shown in Figure 12b achieved CEH from 88% to 99.5%. Using the N-heterocycle-based membranes shown in Figure 12c, CEH of 98% to 99.8% were realized. In fluoro-carbon-based membranes VRFB cells with MS135 (FPAE, dhe, CEM), MS111 (ETFE, dho, AIEM), MS93 (PTFE, sym, -) and MS97 (PVDF, sym, -) also achieve high CEH of at least 98%. In hydro-carbon-based membranes VRFB cells with MS219 (PPSU, dhe, AIEM*), MS214 (PPSU, dho, AEM), MS250 (PPE, dho, AEM), MS225 (PES, asym, CEM), MS228 (PES, dhe, CEM), MS194 (PEEK, dho, AEM), MS227 (PES, asym, AIEM*), MS205 (PSU, sym, AEM), MS226 (PES, sym, AIEM), MS166 (PEEK, dho, CEM), MS229 (PES, asym, CEM), MS249 (PF, dho, CEM), MS173 (PEEK, dhe, CEM), MS170 (PEEK, dho, CEM), MS251 (PPE, dho, AEM) and MS252 (PPE, dho, AEM) reach high CEH of at least 98%. For the N-heterocycle-based membranes all VRFB cells shown reach CEH of at least 98%. These include MS269 (PBI, asym, AEM*), MS262 (PBI, dho, AEM*), MS264 (PBI, dho, AEM*), MS299 (PI, dho, CEM), MS300 (PI, dho, CEM), MS320 (PI, dho, CEM), MS296 (PI, dho, CEM) and MS270 (PBI, sym, AEM*). Low CEH were measured with MS109 (ETFE, dho, CEM), MS145 (PEEK, dho, CEM) and MS221 (PES, sym, CEM). It can be assumed that the water uptake of 181% for MS109 and 88% for MS145 as well as large pores for MS221 during cycling led to excessive electrolyte transfer and thus to charge loss. Lower Dc measured for the membranes in Figure 12 enable higher coulombic efficiencies. For example, in contrast to MS145 (Dc = 3.06 × 10−6/CEH = 93%) higher CEH are realized with MS162 (Dc = 1.04 × 10−7/CEH = 97%), MS163 (Dc = 1.67 × 10−7/CEH = 99%) and MS173 (Dc = 3.5 × 10−7/CEH = 99%) at the same current density of 200 mA cm2. Figure 13 shows the voltage efficiencies (VEH) of VRFB cells with current densities of at least 100 mA cm−2 using the specified membrane samples. The VEH of VRFB cells using the fluorocarbon-based membrane samples shown in Figure 13a ranges from 65% to 92%. VEH of 61% to 99% are achieved using the hydro-carbon-based membranes shown in Figure 12b and VEH of 53% to 78% using the N-heterocycle-based membrane samples shown in Figure 12c. High VEH of at least 80% are measured with MS134 (FPAE, dho, CEM), MS135 (FPAE, dhe, CEM), MS117 (PFSA, dhe, CEM), MS251 (PPE, dho, AEM), MS252 (PPE, dho, AEM), MS209 (PSU, sym, AEM), MS142 (DAPP, dho, AEM), MS250 (PPE, dho, AEM), MS214 (PPSU, dho, AEM), MS209 (PSU, sym, AEM), MS228 (PES, dhe, CEM), MS164 (PEEK, dho, CEM), MS225 (PES, asym, CEM), MS226 (PES, sym, AIEM), MS229 (PES, asym, CEM) and MS145 (PEEK, dho, CEM). For VRFBs equipped with N-heterocycle-based membranes, the highest VEH with MS269 (PBI, asym, AEM*) is 78.5%, with MS263 (PBI, dho, AEM*) and with MS270 (PBI, sym, AEM*) 78%. With the exception of MS270 in Figure 13c, the results in Figure 13a–c show the tendency of the VEH to decrease with increasing current density. Figure 14 shows the energy efficiency (EEH) of VRFB cells with a current density of at least 100 mA cm−2 using the specified membrane sample. Energy efficiencies of 63% to 89.5% were achieved with fluoro-carbon-based membranes, 57.2% to 92% with hydro-carbon-based membranes and 52.5% to 78.4% with N-heterocycle-based membranes. Using fluoro-carbon-based membranes, VRFB cells with MS134 (FPAE, dho, CEM) achieve an EEH of 89.5% at a current density of 100 mA cm−2, with MS135 (FPAE, dhe, CEM) an EEH of 87.7% at a current density of 100 mA cm−2 and with MS117 (PFSA, dhe, CEM) an EEH of 81% at a current density of 120 mA cm−2 at a current density of 100 mA cm−2. Using hydro-carbon-based membranes, VRFB cells can be obtained with MS251 (PPE, dho, AEM), MS252 (PPE, dho, AEM), MS250 (PPE, dho, AEM), MS214 (PPSU, dho, AEM), MS225 (PES, asym, CEM), MS228 (PES, dhe, CEM), MS226 (PES, sym, AIEM), MS229 (PES, asym, CEM) and MS142 (DAPP, dho, AEM) and have an EEH of at least 80%. In VRFB cells with N-heterocycle-based membranes, the highest EEH are between 70% and 80%. MS269 (PBI, asym, AEM*), MS263 (PBI, dho, AEM*), MS270 (PBI, sym, AEM*) and MS320 (PI, dho, CEM) were used. Figure 15 shows the EEr (calculated with the reference membrane from Table 5, Table 6, Table 7, Table 8, Table 9, Table 10, Table 11, Table 12, Table 13 and Table 14) of VRFB cells and the respective publication year.
Figure 15

Energy efficiency ratios in recent years: (a) fluoro-carbons, (b) hydro-carbons and (c) N-heterocycles.

An EEr of 0.901 to 1.250 is obtained with fluoro-carbon-based membranes, an EEr of 0.907 to 1.305 is obtained with hydro-carbon-based membranes and an EEr of 0.919 to 1.220 is obtained with N-heterocycle-based membranes. With MS118 (PFSA, dhe, CEM), MS121 (PFSA, dhe, CEM), MS126 (PFSA, dhe, CEM) and MS92 (PTFE, dhe, CEM), an EEr of at least 1.1 was achieved for the fluorocarbon-based membranes. The hydro-carbon-based membranes were tested with MS219 (PPSU, dho, AIEM*), MS161 (PEEK, dhe, CEM), MS136 (DAPP, dho, CEM), MS151 (PEEK, dhe, CEM), MS150 (PEEK, dho, CEM), MS172 (PEEK, dhe, CEM), MS160 (PEEK, dho, CEM) and MS157 (PEEK, dho, CEM) and achieved a high EEr of at least 1,1. Among others, MS320 (PI, dho, CEM), MS269 (PBI, asym, AEM*), MS313 (PI, dhe, AIEM*), MS266 (PBI, sym, AEM*), MS298 (PI, dho, CEM), MS301 (PI, dho, CEM) and MS317 (PI, dhe, AIEM*) achieved a high EEr of at least 1.1. Potential for improvement of the VRFB can be seen especially in the hydro-carbon and N-heterocycle-based membranes in Figure 15b,c. This improvement represented by EEr is also observed with the fluoro-carbons, however, in weaker expression. In conclusion, Figure 15 and Table 15 both show that membrane change often leads to improved energy efficiency under otherwise identical test conditions.
Table 15

High energy efficiency ratios.

MSPolymer UsedEErCDDrdWUIECRef.
-mA cm−2-µmwt.%mmol g−1
219PPSU1.305100-50-1.2[34]
118PFSA1.250800.5-310.925[112]
320PI1.220100-150-0.4[213]
121PFSA1.210800.0521723.60.97[131]
269PBI1.20680----[194]
261other1.20020----[191]
161SPEEK1.200600.0618020.70.86[72]
136sDAPP1.181200-41-1.8[139]
139qDAPP1.181200-54-1.2[139]
184SPEEK1.179300.179-221.08[147]
126PFSA1.17770-19314.30.92[134]
151SPEEK1.175400.16837211.44[33]
313PI1.167400.1045044.21.16[210]
298PI1.160600.055-17.81.5[207]
92PTFE1.155800.452565.5-[115]
Publications show, in part, the influence of the polymer and membrane properties on VRFB cell performance. Water uptake and the degree of functionalization can be optimized by the use of cross-linkers [35]. An optimum of 18% (WU) is determined for the PPE-based membranes (dho, AEM) [35]. At this optimum and a current density of 100 mA cm−2 the maximum CE, VE and EE is 97.7%, 94% and 92%. Here, an EEr of 1.045 compared to N212 can be achieved. Permeability can be improved by introducing positive charges into the polymer [162]. This leads to the ability of the membrane to keep CE high and self-discharge of a VRFB cell low. An important property of polymer membranes is the ion-selectivity which can be determined by proton conductivity and permeation experiments. This selectivity can further be optimized by adjusting the thickness of CEM [113] to maximize the CE, VE and EE of the VRFB cell. Ionically cross-linked blend membranes [34] represent one of the well-balanced compromises regarding these properties. The ionic cross-linking of PBI and sulfonated PPSU enables reduced water uptake combined with comparatively high IECc and high proton conductivity. This type of membrane with a thickness of 50 µm enables a high EE of 77% and an EEr of 1305 compared to N117 at 100 mA cm−2. Good results can also be achieved with PBI membranes containing enhanced targeted porous structures. Using symmetric porous structures, PBI membranes from [193] and [195] enable energy efficiencies of 87% and 90%. The asymmetrically porous PBI membrane from [194] enables a comparatively high energy efficiency of 82% as well. Furthermore, it is possible to design porous membranes with neutral polymers such as PVDF (MS99, asym) or PTFE (MS93, sym). These appear to have improved long-term stability [91,118]. While Table 5, Table 6, Table 7, Table 8, Table 9, Table 10, Table 11, Table 12, Table 13 and Table 14 provide an exhaustive list of EEr values, Table 15, for the sake of brevity, contains only the fifteen flow-battery targeted membrane samples which showed the highest values during our investigation.

5. Cycle Stability

Various methods are used to evaluate the stability of membranes. It is possible to determine the weight loss over time at a certain temperature by way of mass balance. This is done using swelling tests in aggressive media such as Fenton’s reagent or charged VRFB catholytes. Another method is VRFB cycling tests, which plot the achieved battery performance over a number of cycles graphically. This test is performed to evaluate the stability of the membrane for a given number of cycles [144] or to determine the time of failure of the membrane [206]. Table 16 shows results of VRFB’s cycling tests. In most cases, a current density of 40–80 mA cm−2 was used to show cycle stability. Cycle stability at current densities of 120–200 mA cm−2 was demonstrated in some cases [35,45,74,103,134,199]. Furthermore, the electrolyte quantities in these cycling tests varied. A comparatively high cycle stability of 13000 cycles was demonstrated with a symmetrically porous PBI membrane [195]. A total of 6000 cycles were achieved with a symmetrically porous PSU membrane (AEM, cross-linked) [102]. 4000 charge/discharge cycles were performed with a partially fluorinated and vinylimidazole-based AEM [41]. 1000 cycles were completed with an asymmetrically porous PVDF membrane [118] and a sPEEK-based cation exchange membrane [144]. Many other results with cycles between 50 and 13,000 can be found in Table 16.
Table 16

Cycle stability of published membrane samples.

PolymerMSCyclesmL | mA cm2Ref.PolymerMSCyclesmL | mA cm2Ref.
PTFE94700- | 80[88]PES2247040 | 80[174]
PVDF975030 | 80[117]23010080 | 50[176]
98100030 | 80[118]PPE25150025 | 200[35]
9930030 | 80[119]other2544000- | 50[41]
10223040 | 60[68]2551503 | 40[186]
PFSA11615060 | 80[64]2565003 | 40[187]
117300- | 120[130]2591203 | 20[190]
DAPP143400100 | 50[43]PBI262200100 | 50[65]
PEEK15512050 | 60[58]2701300060 | 80–120[195]
15710050 | 80[60]27130010 | 60[87]
16130010 | 30[72]27222020| 30[63]
1671000- | 80[144]PPEK290100120 | 50[79]
17418030 | 80[59]29110030 | 60[61]
17650050 | 80[145]PI29650030 | 30–120[74]
1805050 | 60[38]29775030 | 50[206]
19410030 | 80[98]298100- | 60[207]
PSU204900- | 80[162]30110060 | 60[78]
2056000100 | 120[102]31150030 | 25–70[209]
20750050 | 80[163]3131008 | 40[210]
20830030 | 80[164]3171008 | 40[211]
PES22015030 | 80[171]Nafion3220050 | 160[45]
22125060 | 80[172]5620050 | 160[45]

6. Membrane Costs

The cost of a VRFB varies with its electrical power (stack size) and available storage capacity (volume of battery electrolyte). The cost proportion of the installed components can therefore vary greatly. A cost analysis conducted by the U.S. Department of Energy (DOE) showed that the cost proportion of the membrane, measured against the total system, is 44% for a plant with a storage capacity of 0.25 MWh and 27% for a plant with a storage capacity of 4 MWh [35]. The cost proportion of the system is stated to be even lower at 10–15% in [65]. In relation to the stack costs, however, a cost proportion of about 40% has been assumed for the use of Nafion [52,65,86,92,185,193,197], whereby also cost ranges of 30–50% of the stack were mentioned [144]. The high specific cost of Nafion (500–800 USD m−2) [86,189] is reported disparately, since with decreasing mass per square meter and different membrane thickness (50.8 µm to 183 µm) as well as different purchase quantities, the price varies. In [46] is mentioned that a quantity of 0.3 × 20 m2 N212 is about 50% cheaper than N115. In [163] N212 is quoted at 225 USD m-2. Referring to [46] this results in a cost saving of 12% to 25% if N212 is preferred to a N115 membrane. Substituting the N115 membrane for a Vanadion membrane reduces the cost from 331 USD kWh−1 to 251 USD kWh−1 for a 1 MWh plant [27]. Furthermore, rough cost estimates are given for published flow-battery targeted membranes. It is assumed that a PES-based membrane is about 1/10 of the price of N115 [174]. PEEK are generally said to have lower production costs due to the aromatic main chain [33]. For PPSU-based membranes, the price could be about 1/400 of Nafion [48]. For partially fluorinated sulfonated PI membranes the manufacturing cost is 167 USD m−2 [206]. With material costs of 100 USD m−2, the cost of PAEK membranes appears to be lower than the cost of Nafion [152]. The cost for PSU membranes is 21 to 24 USD m−2 [163]. Further, when using PSU membranes, a cost saving of 1/20 compared to Nafion is reported [165]. Table 17 gives an overview of low-cost flow-battery targeted membranes in recent years.
Table 17

Published low-cost membranes.

MSMembrane PolymerRef.MSMembrane PolymerRef.
224PES[174]129PFSA[136]
151PEEK[33]167PEEK/PTFE[144]
263PBI[65]93PTFE[91]
191PEEK[150]98PVDF[118]
217PPSU[48]251PPE[35]
297PI[206]207PSU[163]
266PBI[193]286PPEK[204]
243PF[181]209PSU[165]
258Other[189]10PFSA[27]
C. Minke et al. have dealt with the costs of VRFB, in particular the costs of membranes more extensively. This is how a cost proportion of 37%, for a 250 kW stack using Nafion membrane, is calculated [214]. The use of sPEEK membranes could reduce the cost proportion to 8%. This would reduce the cost of a 250 kW stack from 219,000 EUR to 150,000 EUR. They also describe that the specific price of membranes depends on the production volume. A calculation in [215] shows that the price of Nafion can be reduced from 300 USD m−2 to approximately 20 USD m−2 if the production quantity is increased from 0.01 to 10 million square meters per year. The comprehensive listing of membrane costs in [10] describes a current cost range of 16–451 EUR m−2. Looking at the raw material prices in the plastics industry, differences can be seen in the specific costs for polymer granulates, which are used in various flow-battery targeted membranes. The Cambridge Engineering Selector database [216] provides an overview (Figure 16). PS and PP are traded at significantly less than 5 EUR kg−1. PSU, PES, ETFE, PVDF, PTFE and PPSU are traded in the range from 10 to 12 EUR kg−1. The high-performance polymers PEEK, PEK, PEKK and PI range from 70 to 110 EUR kg−1.
Figure 16

Commercial polymer products: specific costs and maximum service temperature [216].

7. Conclusions

By now, numerous flow-battery targeted membranes for the VRFB exist. Most developments show improved VRFB performance when compared to VRFB equipped with reference (Nafion) membranes. Less often, the stability of membranes is investigated at high cycles of significantly more than 1000. From a technical point of view, information on this has a similar significance as the demonstration of VRFB performance with a new membrane. When stating costs, only rough estimates can be made usually. The cost of up scaling, e.g., choice and planning of production technology, are often not taken into account. Fundamental examples of the influence of membrane properties on VRFB performance were described in Section 4.2. They can be considered as an approach for the development of membranes based on other, cheaper or chemically more stable polymers. Results from PFSA membrane modifications lead to the conclusion of improved VRFB performance. These modifications, however, may lead to increased production costs through potential additional steps during manufacturing. PFSA membranes are known for their chemical stability, which was also demonstrated in cycling tests with new “low-cost” or fluorine-free membranes. 1000 and more charge and discharge cycles were achieved with MS98 (PVDF, asym, -), MS167 (PEEK, dhe, CEM), MS205 (PSU, sym, AEM), MS254 (QPTM, dho, AEM) and MS270 (PBI, sym, AEM*). A lot of membrane modifications can be found in hydro-carbon-based membranes, where DAPP is investigated in addition to commercially available PEEK or PSU. Which part of a performance improvement can be attributed to a specific membrane property can generally not be formulated in concrete figures, as these partly influence each other. For example, changes in ion-exchange capacity lead to changes in swelling properties, which affect thickness, water uptake and ultimately selectivity. For cost optimized VRFB manufacturing, membrane production must be a continuous process on an industrial scale. In addition to investment and operating costs, raw material prices are a large influence for the specific costs of membranes produced in a large scale. In order to determine the material costs, it is therefore necessary to know the material composition of the membrane and the amount of operating materials required for all production steps. On the basis of the data from this study, we conclude that some suggestions with reference to membrane type for different operating modes of the VRFB can be made. Dense AEM and N-heterocycle-based membranes, especially PBI membranes, are suitable for lowest discharge of the VRFB. Symmetric and asymmetric porous membranes as well as CEM enable VRFB operation at high current densities. AIEM and dense heterogeneous CEM are the choice for operation mode with highest energy efficiency (Table 18). The cost column in Figure 16 shows the specific cost range for the three material groups fluorocarbon, hydro-carbon and N-heterocycle-based membranes. Of course, PVDF and ETFE-based materials are in the cost range of PSU or PES (Figure 16), but the expansive PFSA materials increase the average value. The manufacturing of dense polymer films is generally easier and cheaper than making membranes with a special porosity.
Table 18

Evaluation matrix of polymer membranes (+ less good, ++ good, +++ best).

Membrane Chemistry and StructureEfficiencyMembrane Material and StructureCost
CEVEEE
CEM++++++fluoro-carbon+
AEM++++++hydro-carbon+++
AIEM+++++++N-heterocycle++
dense++++++++dense+++
sym++++++sym++
asym++++++asym++
VRFB performance, high chemical stability and reduced costs will continue to play an important role in future membrane research. For promising membrane developments, long-term cycling experiments are recommended, whereby the membrane is examined before and after with regard to its chemical and structural change. There is still research potential in the choice of materials for membrane development using polymer products with a price well below 10 EUR kg−1. For lithium-ion batteries a list of different coated porous polyolefin separators was published in 2016 [217]. The Poly(ethylene) (PE), poly(propylene) (PP) and PE/PP-based low-cost separators can be a good starting material for making VRFB membranes, too. In 2020 such a kind of VRFB membrane was made by coating a hydrophilic poly(ethylene) separator with PBI [198]. The influence of the membrane composition regarding proton conductivity and vanadyl permeation is relatively well known, but the influence of the membrane structure is mostly unknown. Future research and development approaches could include the in-depth investigation of membrane structures and their influence on VRFB performance. This is seldom considered regarding ion-exchange membranes, even though dense CEM, AEM or AIEM also have electrolyte-filled pores and channels. The use of commercial polymers is just as advantageous as the use of polymerizable monomers. If large production quantities are considered, the question also arises as to what a suitable recycling concept for discarded membranes could look like. If these membranes were to be selected for thermal recycling, fluorine-free materials would lower cost. This should also be taken into account for other membrane additives. Future efforts to enhance the design of membranes for VRFB could still be the development of new polymer materials as well as manufacturing technology innovations. Generally, some “simple” and fundamental facts should be taken into account, when designing membranes for VRFB-based on polymers: Dimensional stability after soaking the dry membrane in battery electrolyte or water is very important to keep the ion channels diameters as small as possible. For sulfonated polymers as a proton conductor in the membranes, it should be taken into account that its acidity is dependent on the polymer used and influences the proton conductivity. The thickness of the membrane (length of ion channels) should be optimized for high selectivity. As many ion channels as possible should be aimed for good conduction between the two half-cells. The polymer chemistry of a membrane and its interaction with the battery electrolyte not only, but also the membrane morphology allow special membranes for enhanced VRFB performance in low self-discharge, high current density or high energy efficiency mode. The degree of sulfonation and covalent or ionic cross-linking of polymers are important methods to enhance the membrane morphology. This was shown with some membranes mentioned in this study. Polymer cross-linking should be focused when designing membranes with high degree of sulfonation. Additionally, self-ordering polymers, like copolymers or polymers with crystalline proportions could be an option to control membrane morphologies on a molecular scale or to enhance its chemical stability. Manufacturing technology could include dielectrophoresis units to enhance the design of membranes, too. Dielectrophoresis is a method to separate materials with different dielectric properties. Due to the fact that composite membranes, containing a proton conductor and, e.g., a hydrophobic matrix, consist of materials with different dielectric constants it is possible to align the proton conductor as ion channels between the two surfaces of a flat sheet membrane in an electric field during manufacturing. This might influence proton conductivity and H+/V selectivity. Furthermore, it might be possible to increase the resistance to the highly oxidizing electrolyte of the positive half-cell by additional coating strategies.
  19 in total

Review 1.  Membrane development for vanadium redox flow batteries.

Authors:  Birgit Schwenzer; Jianlu Zhang; Soowhan Kim; Liyu Li; Jun Liu; Zhenguo Yang
Journal:  ChemSusChem       Date:  2011-10-17       Impact factor: 8.928

2.  Ion conducting membranes for aqueous flow battery systems.

Authors:  Zhizhang Yuan; Huamin Zhang; Xianfeng Li
Journal:  Chem Commun (Camb)       Date:  2018-07-05       Impact factor: 6.222

3.  Insights into the Impact of the Nafion Membrane Pretreatment Process on Vanadium Flow Battery Performance.

Authors:  Bo Jiang; Lihong Yu; Lantao Wu; Di Mu; Le Liu; Jingyu Xi; Xinping Qiu
Journal:  ACS Appl Mater Interfaces       Date:  2016-05-05       Impact factor: 9.229

Review 4.  Porous membranes in secondary battery technologies.

Authors:  Wenjing Lu; Zhizhang Yuan; Yuyue Zhao; Hongzhang Zhang; Huamin Zhang; Xianfeng Li
Journal:  Chem Soc Rev       Date:  2017-04-18       Impact factor: 54.564

5.  Investigation of local environments in Nafion-SiO(2) composite membranes used in vanadium redox flow batteries.

Authors:  M Vijayakumar; Birgit Schwenzer; Soowhan Kim; Zhenguo Yang; S Thevuthasan; Jun Liu; Gordon L Graff; Jianzhi Hu
Journal:  Solid State Nucl Magn Reson       Date:  2011-11-22       Impact factor: 2.293

6.  Influences of permeation of vanadium ions through PVDF-g-PSSA membranes on performances of vanadium redox flow batteries.

Authors:  Xuanli Luo; Zhengzhong Lu; Jingyu Xi; Zenghua Wu; Wentao Zhu; Liquan Chen; Xinping Qiu
Journal:  J Phys Chem B       Date:  2005-11-03       Impact factor: 2.991

7.  Durable and Efficient PTFE Sandwiched SPEEK Membrane for Vanadium Flow Batteries.

Authors:  Lihong Yu; Jingyu Xi
Journal:  ACS Appl Mater Interfaces       Date:  2016-09-01       Impact factor: 9.229

8.  Hydrophobic asymmetric ultrafiltration PVDF membranes: an alternative separator for VFB with excellent stability.

Authors:  Wenping Wei; Huamin Zhang; Xianfeng Li; Hongzhang Zhang; Yun Li; Ivo Vankelecom
Journal:  Phys Chem Chem Phys       Date:  2012-12-05       Impact factor: 3.676

9.  Morphology and electrochemical properties of perfluorosulfonic acid ionomers for vanadium flow battery applications: effect of side-chain length.

Authors:  Cong Ding; Huamin Zhang; Xianfeng Li; Hongzhang Zhang; Chuan Yao; Dingqin Shi
Journal:  ChemSusChem       Date:  2013-06-14       Impact factor: 8.928

10.  A Low-Cost and High-Performance Sulfonated Polyimide Proton-Conductive Membrane for Vanadium Redox Flow/Static Batteries.

Authors:  Jinchao Li; Xiaodong Yuan; Suqin Liu; Zhen He; Zhi Zhou; Aikui Li
Journal:  ACS Appl Mater Interfaces       Date:  2017-09-15       Impact factor: 9.229

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Review 1.  TiO2 Containing Hybrid Composite Polymer Membranes for Vanadium Redox Flow Batteries.

Authors:  Gowthami Palanisamy; Tae Hwan Oh
Journal:  Polymers (Basel)       Date:  2022-04-15       Impact factor: 4.967

2.  The Application of a Modified Polyacrylonitrile Porous Membrane in Vanadium Flow Battery.

Authors:  Lin Qiao; Shumin Liu; Haodong Cheng; Xiangkun Ma
Journal:  Membranes (Basel)       Date:  2022-03-31

3.  Composite Anion-Exchange Membrane Fabricated by UV Cross-Linking Vinyl Imidazolium Poly(Phenylene Oxide) with Polyacrylamides and Their Testing for Use in Redox Flow Batteries.

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