Rokas Sažinas,
Suzanne Zamany Andersen
,
Katja Li
,
Mattia Saccoccio
,
Kevin Krempl
,
Jakob Bruun Pedersen
,
Jakob Kibsgaard
,
Peter Christian Kjærgaard Vesborg
,
Debasish Chakraborty and
Ib Chorkendorff
*
Department of Physics, Technical University of Denmark, Kongens Lyngby, 2800, Denmark. E-mail: ibchork@fysik.dtu.dk
First published on 23rd September 2021
Lithium-mediated electrochemical ammonia synthesis (LiMEAS) in non-aqueous media is a promising technique for efficient and green ammonia synthesis. Compared to the widely used Haber–Bosch process, the method reduces CO2 emissions to zero due to the application of green hydrogen. However, the non-aqueous medium encounters the alkali metal lithium and organic components at high negative potentials of electrolysis, which leads to formation of byproducts. To assess the environmental risk of this synthesis method, standardized analytical methods towards understanding of the degradation level and consequences are needed. Here we report on the implementation of an approach to analyze the liquid electrolytes after electrochemical ammonia synthesis via high-resolution gas chromatography-mass spectrometry (GCMS). To characterize the molecular species formed after electrolysis, electron ionization high-resolution mass spectrometry (EI-MS) was applied. The fragmentation patterns enabled the elucidation of the mechanisms of byproduct formation. Several organic electrolytes were analyzed and compared both qualitatively and quantitatively to ascertain molecular composition and degradation products. It was found that the organic solvent in contact with metallic electrodeposited lithium induces solvent degradation, and the extent of this decomposition to different organic molecules depends on the organic solvent used. Our results show GCMS as a suitable technique for monitoring non-aqueous electrochemical ammonia synthesis in different organic electrolytes.
A typical LiMEAS cell consists of a noble metal anode e.g. platinum (Pt) and transition metal cathode which does not interact or alloy with lithium (Li) e.g. molybdenum (Mo).10,11 The electrodes are usually submerged in the non-aqueous organic electrolyte with or without a membrane or separator. The electrolyte is composed of a conducting Li salt and a solvent, typically lithium perchlorate (LiClO4)12 and tetrahydrofuran (THF), respectively.10,13 Other mostly ether-based solvents, such as dimethoxyethane (DME) or diethyleneglycol dimethyl ether or diglyme (DG) can also be used for LiMEAS. Thus, the influence of the electrolyte on the electrochemical ammonia synthesis and the overall stability have to be addressed in order to overcome limited performance and inhibition of the nitrogen reduction reaction (N2RR).
Due to the complex nature of LiMEAS, no reports on the aging have been introduced so far which can be related to the used materials and components, as well as to the interactive reactions. However, due to the instability issues previously noted,5,11 there is reason to believe that undesirable organic lithium compounds are formed during the chemical reactions of LiMEAS, leading to degradation of the electrolyte. Li metal is both chemically and electrochemically unstable and reacts with traces of moisture, oxygen and organic solvent. Even at room temperature, Li reacts with ethanol (EtOH) forming lithium ethoxide (LiOEt).14 These reactions can lead to hydrolysis and oxidation products inside the electrolyte. Furthermore, under electrochemical operation conditions, a ring opening reaction of the cyclic THF can occur.14 The electrochemical reduction of the organic electrolyte at the anode of lithium ion batteries (LIB) results in the formation of the solid electrolyte interphase (SEI).15 This layer is composed of inorganic and organic decomposition products and is most likely necessary for long-term performance, as it is ideally only permeable for lithium ions, thus protecting the highly reactive anode against further reduction reactions.16–18 The reaction of Li with the solvent leads to the formation of protective SEI, but byproducts dissolved in the electrolyte might encumber the system by increasing contamination.19–22 Thus, the protective nature of this passivation layer could be distinct to prevent further electrolyte decomposition. There are plenty of reports and techniques regarding the monitoring of aging in LIB cells.15,23 Among all of them, the electrolyte aging can be monitored intensively using chromatography techniques including gas chromatography (GC)20,24 and high-resolution mass spectrometry (MS) for structural elucidation along with different ionization techniques.24
In this work, we report on the application of a GCMS method for analyzing and identifying the soluble side-products in the LiMEAS process. This approach with MS detection gives an insight to understand the chemical and electrochemical reactions in non-aqueous LiMEAS qualitatively and quantitatively. The aim of this report is to investigate possible degradation products formed during LiMEAS in the most widely used, efficient, and promising ether-based electrolytes, such as THF, DME and DG. The assessment of individual electrolytes and comparison between each is very important to select the most efficient and stable system for LiMEAS. This report brings the field closer to understanding of the stability and aging effects vital for advancing the technological application of LiMEAS.
A modified colorimetric indophenol method was used to quantify the synthesized ammonia.13,25 The UV/Vis spectroscope (UV-2600, Shimadzu) with absorbance was used to characterize the samples between 400–1000 nm. Each spectrum was analyzed after subtraction of the blank sample solution. The measurements were performed with 0.5 mL sample of the water trap and three 0.5 mL samples from the electrolyte including one sample from the electrolyte for a background spectrum. The difference between the peak around 630 nm and the trough at around 860 nm is used as maximum and minimum, respectively. A fitted curve of the difference between the peak and trough of each concentration showed a linear regression with an R2 value of 0.999. The amount of ammonia in the headspace was quantified by de-gassing the system through an ultra-pure water trap, however revealed to be negligible in the experiments of the current study. The samples were treated as described previously, to determine the ammonia concentration.13
The area of the most intense XIC fragment of the eluting compound was integrated and compared to the main peaks of the main components of the electrolyte, the solvent and EtOH. After integration, the relative amount of compound was estimated and compared to the amount of experimentally added 100 ppm concentration standard in THF. Some of the compounds, especially for DG system were difficult to obtain, so the amount from a standard value is missing. However, the integration of the XICs method for other compounds is in a good agreement with the experimental standards and gives confidence in the evaluated amount of the compound molecule. Further description of the method is given in the ESI.†
Fig. 1a shows the total ion current chromatograms (TIC) of the three selected solvents after LiMEAS. The same chromatogram with higher magnification is represented in Fig. 1b. Mainly two distinct peaks can be seen in the chromatograms, which in general present the main components of the electrolyte for LiMEAS. The first peak at ∼3 min represents ethanol (EtOH) elution, while the most intense peak is the solvent (THF; DME; DG). The small difference in retention time of EtOH is probably due to experimental or instrumental error. The set pressure of carrier He gas was not very stable for the set flow rate in the used system. This and the manual injection and program execution introduced slight differences in EtOH retention time, coupled with contamination of the GC column over time after numerous experiments. From a superficial point of view, no other products can be detected in the chromatograms, except THF. This is because TICs are very dependent on the concentration of the species. Since the solvent and EtOH concentrations are so high compared to the other components, the peak intensities of the latter ones can only be found by analyzing extracted ion chromatograms (XIC) mass-by-mass.
Upon screening XICs by m/z values from 1 to 200, other peaks start to become visible, enabling the discovery of the small amounts of various components present in the systems. No peaks at higher than 200 m/z values were found, that is why 200 m/z was chosen as an end of the scanning range. Fig. 2 shows an example of two different XICs obtained with the set m/z values of 15 and 31. These m/z values represent methyl (CH3+) and methoxyl (CH3O+) or methylene hydroxyl (CH2OH+) organic species, respectively, that are common in many fragmentation patterns of organic molecules of this study supported by NIST database center26 depending of the functional groups. The m/z 15 is found in the molecules containing methyl group, however m/z 31 is present in the molecules containing alcohol or OH functional group. Following the method, more peaks in the chromatograms appear at specific retention time. This means that there are species containing the fragmentation parts with the m/z values of 15 and 31, which elute from the GC system at different and distinct retention time. One can see that both of these m/z values are present in the decomposition of the solvents. This is probably due to the fact that the concentration of the solvent and EtOH is so high that any rational fragmentation species can be detected at the retention time of them.
After LiMEAS in DME, the electrolyte was analyzed by GCMS providing the XIC results as shown in Fig. 3. Fig. 3a shows all the specific XICs with their individual contribution to the TIC at specific retention time, and Fig. 3b represents a mass spectrum of MS scan nr. 994 at 5.57 min retention time with thee overlaid spectrum from NIST database. One can spot that the distinct peak at ∼5.6 min, which was superficially absent in TIC (Fig. 1), is now easily distinguishable in XICs with some specific m/z values to the compound eluting in the GCMS system. In this manner, all the samples were analyzed and fragmentation particle masses recorded. The same procedure was applied for the other m/z from 1 to 200, though not all the m/z contained intensities, only the background or the spikes of contaminant molecules in the system. The rational MS fragmentation of organic molecules was always present at the specific solvent as well as EtOH retention time in all the chromatograms. This brings to the conclusion that the concentration of the solvent was so huge compared to the other components that LiMEAS decomposition products were just shadowed in TIC and impossible to detect. However, one should always remember that TIC is a sum of all the m/z at a specific time (or scan). This is why lots of m/z or peaks are shadowed in the TICs. According to Fig. 3b, the analyzed compound was in a good agreement with the database. However, it is important to remind that we used softer 30 eV ionization compared to 70 eV in NIST database due to instrument limitations – the electron energy was optimized for the instrument and tungsten (W) source filament. This explains why we see more molecular ion signal at 88 m/z compared to the main fragmentation species at 45 m/z as can be seen in the database spectrum. We also see some more species which can be explained by contaminants in the column or system in general. One should remember that the Fig. 3b represents one scan-moment, and the next one is slightly different with respect to m/z intensities. Also, m/z values at 28 and 32 which are nitrogen and oxygen in the system. And in general, NIST database is created with different MS parameters than we use, so it has to be adjusted carefully. Many, though not all, of the structures were supported by the NIST database. However, they were confirmed by the home-made standard sample analysis.
Similar analysis results of peaks at specific retention times for THF and DG are represented in Fig. 4a and b, respectively. The peaks or specific retention times have been chosen randomly. The figures include the m/z values which had at least some intensity to evaluate. The signal strength of each m/z was evaluated by integrating the peaks and the integration results are presented as inset tables. Different m/z values have different intensity of the peaks. Some of the specific peaks are very intensive compared to the others. And this depends on the decomposing compound and ionization energy of the electrons.
![]() | ||
Fig. 4 The extracted ion chromatograms (XIC) vs. retention time of a specific chromatographic peak for (a) THF and (b) DG after LiMEAS. The insets are the integrals of the peaks. |
The ammonia signal in GCMS is mostly overlaying with H2O signal. However, it depends on the GC program used. The current program (Fig. S2†) was optimized not for separating ammonia from H2O, but for analyzing organic volatile species in three different systems. These would be two different experimental programs for GCMS. If the GC program is modified in the way that the dwelling at 50 °C is kept for 6 min and the ramping towards 100 °C is done with 5 °C min−1 steps, ammonia can be separated from H2O. An example of such a chromatogram is given in Fig. S5 in ESI.† However, the GC program had to be optimized and used for analyzing the volatile organic decomposition products in order to save time. With this in mind, the ammonia was quantified by the well-established indophenol method described in the experimental part and literature.13,25
In the following sections, the decomposition products in each of the three different electrolytes are analyzed in more detail. The molecules of the decomposition products were constructed from the fragmentation patterns, relying heavily, but not always, on the NIST database, as the spectra are dependent on the ionization voltage, and therefore might vary in intensity and number of peaks. Also, to proceed further with the validation of the test and capability of the GCMS technique in the current application with the equipment used, we enabled the quantification methodology of the components after a typical LiMEAS in different electrolytes with in-house made standard solutions of the molecules. The consequent results were compared to the integration of the XIC results for the different components. The analysis of the standard solutions was performed individually. This brought high confidence in molecule identification since the retention time matched well. Some of the DG decomposition products were not commercially available, so the amount from a standard value is missing. However, the integration of the XICs method for other compounds agrees well with the experimental standards, providing confidence in the evaluated amount from GCMS and structure of the molecule.
![]() | ||
Fig. 5 The schematic of decomposition products formed after LiMEAS in THF-based electrolyte. The compounds are summarized in Table 1. |
Nr. | Retention time (min) | m/z | Compound namea | GCMS | Standard retention time (min) | From solution (ppm ± 5) | ||
---|---|---|---|---|---|---|---|---|
Area (arb. u.) | Amount (ppm ± 5) | |||||||
a No chlorinated compounds have been detected, which could be associated to transformations of perchlorate anion in the electrolyte.b Water content before LiMEAS according to Karl–Fischer titration. | ||||||||
1 | 3.6–3.7 | 15; 29; 43; 58 | Butane | 4370 | 8 | 3.6–3.7 | 7 | |
2 | 4.4–4.5 | 29; 31; 43; 45; 58; 59; 60 | Acetic acid | 4297 | 8 | 4.4–4.5 | 7 | |
3 | 4.8–5.0 | 15; 16, 29; 45 | — | 2135 | 4 | — | — | |
4 | 5.1–5.3 | 27–29; 31; 37–42; 68–70 | (2,5 or 2,3)-Dihydrofuran | 25![]() |
45 | 5.1–5.3 | 41 | |
5 | 7.0–7.1 | 31; 42; 47; 59; 72; 84 | Furan-2(5H or 3H)-one | 10![]() |
19 | 7.0–7.1 | 17 | |
6 | 9.7–10.0 | 15; 29; 41; 42; 57; 58; 71 | Butyraldehyde | 4766 | 8 | 9.7–10.0 | 8 | |
7 | 10.0–10.2 | 15; 19; 25–27; 29; 30; 31; 37; 39; 40–43;45–47;57–60; 68–72; 75; 88 | 4-Hydroxybutanal or tetrahydrofuran-2-ol | 45![]() |
82 | 10.0–10.2 | 74 | |
8 | 10.6–10.8 | 28; 29; 31; 41; 43; 58 | Propionaldehyde | 32![]() |
59 | 10.6–10.8 | 53 | |
9 | 11.7–11.9 | 28; 42; 55; 87 | Succinaldehyde | 38![]() |
70 | 11.7–11.9 | 63 | |
10 | 12.5–12.8 | 15; 28; 43; 59 | Acetamide | 9096 | 16 | 12.5–12.8 | 14 | |
H2O | 2.2–2.5 | 16; 17; 18 | Water | 71![]() |
145 | 2.2–2.5 | 36b | 150 |
The results for GCMS analysis in THF-based LiMEAS electrolyte are summarized in Table 1. The main decomposition product in THF-based LiMEAS was found to be compound (7) 4-hydroxybutanal or tetrahydrofuran-2-ol. It is difficult to distinguish which exact compound is it by GCMS because both compounds fragment into similar particles by m/z. According to the analysis outcomes described above and visualized in Fig. 4, the m/z values from MS and the names of the decomposition products were constructed. The sector MS used has a very high sensitivity, which allows distinction of many molecules from peaks with weak intensity to be constructed, as can be seen in the example shown in Fig. 5. Notably the experimental MS spectra display a good signal-to-noise ratio. The very sensitive MS analysis unambiguously allowed identifying most of the molecules after LiMEAS dissolved in the liquid electrolyte based on THF. Thus, the capability of this technique for the analysis and identification of the organic molecules is clear.
Table 1 summarizes all the compounds characterized by GCMS at different retention time and their amount in the THF-based electrolyte after LiMEAS. The amount of the compounds was evaluated from the standards of the solutions of the component and from integration of the peaks of XICs. The approach was chosen to integrate the peak in XIC of the most intense fragment species at different retention time and comparison with the integral of the solvent XIC peak. The latter one for THF molecule is at m/z 42. Most of the materials were formed in very small amounts and were detected less than 100 ppm even after 90 C passed through the electrolytes. One can assume that this is very promising because the electrolyte can be considered stable. It is noteworthy that the amounts estimated by the integration of the chromatographic peaks are higher than from experimental standard solutions. This is probably due to overestimation and errors in the models applied for the integration of the chromatographic peaks by MassLynx or OpenChrom software. However, the integration and experimental standard results are in a close proximity to each other.
![]() | ||
Fig. 6 The schematic of decomposition products formed after LiMEAS with DME electrolyte. The compounds are characterized and summarized in Table 2. |
Compound | Retention time (min) | m/z | Compound namea | GCMS | Standard retention time (min) | From standard solution (ppm ± 2) | ||
---|---|---|---|---|---|---|---|---|
Area (arb. u.) | Amount (ppm ± 2) | |||||||
a No chlorinated compounds have been detected, which could be associated to transformations of perchlorate anion in the electrolyte.b Water content before LiMEAS according to Karl–Fischer titration. | ||||||||
1 | 1.4–1.7 | 29; 30 | Formaldehyde | 6114 | 35 | 1.4–1.5 | 30 | |
2 | 1.7–1.8 | 15; 29; 31; 32; 44 | Acetaldehyde | 1117 | 6 | 1.7–1.8 | 5 | |
3 | 3.3–3.4 | 15; 31; 57; 74 | 2-Methoxyethene-1-ol | 561 | 3 | 3.2–3.1 | 2 | |
4 | 4.8–5.0 | 15; 29; 45 | — | 4215 | 24 | — | — | |
5 | 5.6–5.7 | 15; 29; 31; 45; 58; 59; 60; 74; 88; 89 | (Z,E)-1,2-Dimethoxyethene | 203![]() |
1177 | 5.6 | 1012 | |
6 | 7.8–7.9 | 19; 27; 29; 30; 31; 41; 43; 44; 47; 58; 59; 60; 74; 88; 89; 109 | 1,2-Dimethoxyethan-1-ol | 10![]() |
62 | — | — | |
7 | 8.2–8.4 | 29; 45; 58; 90 | Methyl-2-hydroxyacetate | 7743 | 44 | 8.41 | 38 | |
8 | 9.2–9.3 | 29; 31; 43; 45; 58; 59; 60 | Acetic acid | 9528 | 55 | 9.1–9.3 | 47 | |
9 | 9.7–9.8 | 29; 43; 45; 58 | Methoxyethene | 4983 | 28 | 9.7–9.9 | 24 | |
10 | 10.2–10.5 | 29; 31; 43; 45; 58 | Methoxyethane | 9477 | 54 | 10.1–10.2 | 47 | |
11 | 14.1–14.2 | 29; 31; 45; 58; 59; 60; 88; 89 | 2-Methoxyacetamide | 6770 | 39 | 14.0–14.1 | 33 | |
H2O | 2.2–2.5 | 16; 17; 18 | Water | 16![]() |
110 | 2.2–2.5 | 48b | 107 |
The GCMS analysis performed after LiMEAS in DME-based electrolyte is given in Table 2, with the m/z values from MS and the names of the decomposition products constructed. Some of the peaks contained quite considerable amount of m/z values complicating the identification process of the product structure. The NIST database does not contain such complicated compounds which could be identified. Some of the most characteristic values of the compound (5) were presented above in Fig. 3.
The compounds characterized by GCMS at different retention time and their amount in the DME-based electrolyte after LiMEAS are given in Table 2. The quantification of the compounds was performed from the standards and integration of the GCMS peaks as described above for THF. Most of the materials were formed in ppm amounts. The compound (5) was detected in more than 1000 ppm after 90 C passed through the electrolyte, which is unacceptable for the stability for the LiMEAS process. The decomposition of the solvent is quite considerable under the applied experimental conditions, and the electrolyte is determined to not be stable. The product (5) is formed either after the initial Li reaction with methylene group in DME or via oxidation of DME most likely on the counter electrode, as in the case of THF. The rest of the compounds formed in decent and comparable amounts to the THF experiment. As for the THF-based electrolyte after LiMEAS, the integration of GCMS and experimental results match to each other well, however the later ones are higher. On the other hand, it can be seen that the amount of the compounds in THF and DME detected after LiMEAS is the same, reaching 11 different decomposition species. This can most likely be attributed to the similar nature of the solvents as ethers, which are quite stable organic molecules. However, both of these solvents tend to form radicals and peroxides in the presence of oxygen.
![]() | ||
Fig. 7 The schematic of decomposition products formed after LiMEAS with DG electrolyte. The compounds are characterized and summarized in Table 3. |
Compound | Retention time (min) | m/z | Compound namea | GCMS | Standard retention time (min) | From standard solution (ppm ± 6) | ||
---|---|---|---|---|---|---|---|---|
Area (arb. u.) | Amount (ppm ± 6) | |||||||
a No chlorinated compounds have been detected, which could be associated to transformations of perchlorate anion in the electrolyte.b Water content before LiMEAS according to Karl–Fischer titration. | ||||||||
1 | 2.2–2.4 | 28; 29; 30 | Formaldehyde | 4049 | 36 | 2.2–2.3 | 31 | |
2 | 2.5–2.8 | 16; 17; 18; 29 | Ethane | 10![]() |
87 | 2.5–2.6 | 75 | |
3 | 2.6–2.7 | 15; 16; 29; 30; 31; 32; 43; 44 | Acetaldehyde | 2551 | 21 | 2.6–2.8 | 18 | |
4 | 6.5–6.6 | 15; 29; 42; 43; 44; 45 | Formic acid | 7732 | 64 | 6.5–6.6 | 55 | |
5 | 8.5–8.6 | 15; 19; 26; 27; 29; 30; 31; 42; 43; 45; 46; 47; 57; 58; 72; 75 | Diethyl ether | 1189 | 9 | 8.5–8.6 | 8 | |
6 | 9.1–9.2 | 29; 31; 58; 59 | Methoxyethene | 29![]() |
246 | 9.1–9.2 | 211 | |
7 | 9.7–9.9 | 27; 31; 58; 59; 104 | 2-Hydroxyethyl acetate | 2810 | 23 | 9.7–9.8 | 20 | |
8 | 14.6–14.8 | 29; 58; 59; 72; 88 | 2-Methoxyacetamide | 12![]() |
105 | 14.6–14.7 | 90 | |
9 | 16.0–16.1 | 17; 29; 31; 61; 70; 71; 72; 74; 75; 86; 88; 103; 106; 108; 109 | 2-Methoxyethan-1-ol | 23![]() |
191 | 16.0–16.1 | 164 | |
10 | 16.5–16.6 | 15; 26; 27; 29; 31; 41; 43; 44; 45; 46; 47; 57; 58; 59; 60; 70; 71; 72; 73; 86; 88; 89; 90; 103; 106; 108; 118 | 2-(2-Methoxyethoxy)acetaldehyde | 8194 | 68 | — | — | |
11 | 17.2–17.4 | 15; 26; 27; 29; 31; 42; 43; 45; 57; 58; 59; 60; 86; 88; 89; 103; 106; 118 | 2-(2-Methoxyethoxy)ethan-1-amine | 3506 | 29 | — | — | |
12 | 17.9–18.2 | 29; 31; 43; 45; 57; 58; 70; 103; | 2-(Vinyloxy)acetic acid | 9619 | 80 | 17.9–18.2 | 68 | |
13 | 18.7–18.8 | 15; 29; 31; 43; 45; 57; 58; 59; 60; 88; 103 | (2-Methoxyethoxy)ethene | 259![]() |
2157 | — | — | |
14 | 19.5–19.7 | 29; 57; 58 | Oxalaldehyde | 22![]() |
183 | 19.5–19.6 | 158 | |
H2O | 2.2–2.5 | 16; 17; 18 | Water | 10![]() |
106 | 2.2–2.5 | 44b | 98 |
Many of the decomposition compounds are formed in concentrations greater than 100 ppm, especially the compound (13), which is detected with >2000 ppm after LiMEAS. This DG-based electrolyte seems to decompose the most compared to THF and DME, and is therefore the least stable solvent for the LiMEAS. It decomposes into the most numerous different products after LiMEAS, and the measured concentrations of each of them are considerably large. Most likely this can be attributed to the reactivity of Li towards methylene groups (–CH2–) adjacent to O-atoms in DG, which leads to increased decomposition of the materials. Based on this, the longer the chain in the polyether-based organic solvent in LiMEAS, the worse the stability of the electrochemical system it seems.
Other molecules with higher m/z values than 200 or the polymeric species formed during LiMEAS could not be detected in the GCMS analyses performed in this study, due to the fact that polymers are high boiling point materials. The chromatographic columns cannot sustain temperatures higher than 300 °C. This is why it is difficult to characterize polymers and other high boiling point molecules by GCMS.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/d1ra05963g |
This journal is © The Royal Society of Chemistry 2021 |