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Johnson Matthey Technol. Rev., 2021, 65, (2), 170


Oxygenated Transport Fuels from Carbon Dioxide

Driving towards Net Zero

  • Peter Styring*, George R. M. Dowson
  • UK Centre for Carbon Dioxide Utilisation, Department of Chemical & Biological Engineering, Sir Robert Hadfield Building, The University of Sheffield, Sheffield, S1 3JD, UK
  • *Email:

Article Synopsis

The restructuring of the economy post-COVID-19 coupled to the drive towards Net Zero carbon dioxide emissions means we must rethink the way we use transport fuels. Fossil-carbon based fuels are ubiquitous in the transport sector, however there are alternative synthetic fuels that could be used as drop-in or replacement fuels. The main hurdles to achieving a transition to synthetic fuels are the limited availability of low-cost carbon dioxide at an appropriate purity, the availability of renewable hydrogen and, in the case of hydrocarbons, catalysts that are selective for small and particular chain lengths. In this paper we will consider some of the alternative fuels and methods that could reduce cost, both economically and environmentally. We recommend that increased effort in the rapid development of these fuels should be a priority in order to accelerate the possibility of achieving Net Zero without costly infrastructure changes. As ground transportation offers a more straightforward approach legislatively, we will look at oxygenated organic fuels as an alternative drop-in replacement for hydrocarbons.


The concepts of carbon dioxide utilisation (CDU) and carbon capture and utilisation (CCU) are not new (1). The first recorded example of a CCU process dates back to the 18th century when Joseph Priestly recorded the capture of ‘fixed air’ (CO2) from Leeds Brewery 1768 (2). The process was so successful that Priestly sold what would be now known as the intellectual property (IP) to Jacob Schweppe. To this day the Schweppes Tonic Water labels contain the strapline “creator of bubbles since 1783”. Salicylic acid, a precursor to aspirin was first synthesised from CO2 in 1898. However, it is the synthesis of urea fertiliser from CO2 and ammonia (Figure 1) that highlights a major issue in CCU. If we look at the complete supply chain in reverse, we need ammonia to react with CO2. The ammonia comes from the catalytic reduction of nitrogen using hydrogen, which typically comes from steam methane reforming (SMR). In the SMR reaction, methane reacts with water at high temperature and pressure, over a catalyst, to give hydrogen and CO2 as shown in Equation (i):


Fig. 1

Synthesis of ammonia using Haber-Bosch and Bosch-Meisner chemistry

Synthesis of ammonia using Haber-Bosch and Bosch-Meisner chemistry

If we consider the synthesis of transport fuels from CO2 then the same problem exists: we need hydrogen to reverse the combustion process. If we consider the synthesis of hydrocarbons (3) built from multiple methylene groups, then the stoichiometry is shown in Equation (ii):


As the chain length increases, so does the total hydrogen requirement and this also highlights another important issue. While three equivalents of hydrogen are required to reduce each CO2 molecule, only one equivalent is incorporated in the fuels while two equivalents produce water. If we consider diesel to be C18H38, then a total of 55 equivalents of hydrogen are required for each diesel molecule, also resulting in 36 molecules of water being produced. While synthetic hydrocarbons will become an essential component in the transition of aviation jet fuel from fossil-based to synthetic (4), engines used in ground transportation are more tolerant to a more diverse range of chemical species and are less stringently legislated. Of particular interest are oxygenated fuels such as alcohols and ethers (5). As the energy of a fuel is directly related to the hydrogen content, and so for hydrocarbons the number of C–H bonds, addition of heteroatoms such as oxygen will result in a dilution of the energy density (Table I). However, there is a balance between the relative energy density and the number of carbons, and consequently hydrogen, in the fuel.

Table I

Specific Energy and Energy Density of Selected Fuels that are Derived from Fossil Oil or Can Be Synthesised from CO2 or Other Waste or Bio-Based Carbon Sources (6, 7)

Fuel Reference Specific energy, MJ kg−1 Energy density, MJ l−1
Heavy fuel oil (6) 41.8 41.0
LPG (7) 50.2 25.4
Diesel (7) 45.6 38.6
Gasoline (6) 46.4 34.2
Jet-A (7) 46.4 36.7
Methanol (6) 23.0 18.2
DME (7) 31.7 21.0
Butanol (6) 37.3 30.2

In this paper we consider the energy-carbon balance using methanol, butanol and oxymethylene ethers as exemplars. We consider the pros and cons and suggest avenues for future research where catalysis lies at the centre.

Oxygenated Synthetic Transport Fuels

Methanol Synthesis

The direct transformation of CO2 to methanol requires the addition of three equivalents of hydrogen to generate methanol and water from CO2. This can be performed at moderate temperatures and pressures (220–250°C and 10–30 bar) over heterogeneous metal oxide catalysts, particularly copper and zinc oxides with alumina (CZA, Cu/ZnO/Al2O3), which are based on catalysts that date back to the 1930s (8, 9). This process is now being carried out commercially by Carbon Recycling International, producing 4000 tonnes a year of sustainable methanol from Icelandic geological CO2 and geothermal energy (10).

For this direct conversion, heterogeneous copper-based catalysts are the most extensively studied with catalyst performance thought to be generally dependent on the structure of the copper surface and also possibly the interface between the copper and the other transition metal components, most commonly zinc, zirconium or their oxides (11). Further weight is also given to the degree of dispersion of the copper within the catalyst structure, with increasing copper dispersion and thus copper surface area correlating directly with increased methanol yield (12).

Computational studies have suggested that CO2 reactions on the stepped and close-packed Cu(211) representative surface gives the primary low-temperature reaction pathway via both formic acid and formaldehyde, the route via CO being an alternative and potentially competitive route (13). This CO, generated by the reverse water gas shift reaction (RWGS) can be problematic, particularly at higher temperatures, where excess carbon monoxide is generated from CO2 and hydrogen (see Figure 2).

Fig. 2

A generalised scheme showing the various routes for production of methanol from CO2

A generalised scheme showing the various routes for production of methanol from CO2

Both the CO and the byproduct water can limit the selectivity to and yield of the desired methanol product, especially where carbon monoxide side production increases and the RWGS reaction dominates (14). While the water that is inevitably generated while the reaction proceeds can sinter and degrade the catalyst alone, high CO and H2 concentrations from the RWGS reaction have also been shown to overly reduce these copper surfaces, making sintering happen more easily (15, 16). Additionally, the excess CO production typically promotes hydrocarbon and also higher-alcohol generation via well-understood Fischer-Tropsch chemistry, further increasing hydrogen consumption and complicating product purification (17, 18). However, as discussed in the later section of this article, the production of higher alcohols and other products directly from CO2 by taking advantage of the greater propensity for CO to form new C–C bonds on these catalyst surfaces might be a way to generate CO2 fuels more effectively than individual production of methanol and then carrying out subsequent dimethyl ether (DME), methanol to gasoline (MTG) or methanol to olefins (MTO) processes, thereby avoiding multiple individual processes (19).

One method used to avoid CO production and to generally promote milder reaction conditions is the use of precious metal catalysts such as palladium or platinum instead of, or in addition to, the traditional copper as these help to reduce the required temperature for the reaction and therefore increases reaction selectivity as the RWGS reaction is less favourable (20, 21). In addition, these catalysts can promote the hydrogenation of any CO to methanol, further reducing the CO:CO2 ratio within the reaction mixture (22). However, these catalysts typically show poor CO2 conversion, thought to be due to the lower strength of the bonding between the CO2 and metal surface (23). Yet another approach is to use copper encapsulated in metal organic framework (MOF) catalysts which further promote the exclusion of water from the catalyst surface, increasing the catalyst turnover number. The frameworks can also increase the effective surface area of the active copper species by limiting the growth of the metal surface, a result that can also be achieved by using a hydrotalcite-like compound as the catalyst precursor (24).

For the indirect production of methanol, the RWGS reaction can alternatively be harnessed to generate CO as an intermediate that can then be used to create a sustainable synthesis gas (syngas). This syngas can then be used for methanol production separately. Using CO in this way has the benefit of very high selectivity (over 99.5%) and high yield, facilitated by the absence of water byproduction (which in this case would be removed during CO formation) and the fact that CO is a more reactive starting material than CO2 (25). In some cases, when producing methanol from CO, the product methanol solution could even be used for further product generation without additional purification or drying (26). It is due to these advantages that general industrial (non-sustainable) methanol production typically uses this syngas route, and it supplies the overwhelming majority of the global methanol demand, which was 83 million tonnes in 2019 (27). The routes for creating the CO starting material from CO2 are numerous, including classic hydrogenation (RWGS), disproportionation reactions with biochar (where elemental carbon reacts with carbon dioxide to form two equivalents of CO), electrochemical and even plasmolytic routes (2831).

Butanol Synthesis

Compared with methanol, producing the four-carbon chain butanol from CO2 is a far more challenging synthesis. However, butanol is a valuable potential ‘drop-in’ replacement for petrol as a liquid transport fuel and is compatible with existing fuel infrastructures. It can even be used alone as fuel for unmodified vehicles, with an octane number of 96 (32). It is hydrophobic enough to prevent water and salt corrosion in modern engines, which is a major drawback when using high ethanol content in road vehicle fuel in much of the world (33). Butanol in standard petrol engines has also been shown to have similar or even superior fuel economy than the petrol it replaces, despite having approximately 11% less energy density. This is due to its nature as a single-component fuel, rather than the wildly diverse mixture of compounds that make up fossil fuels, with the entirety of the fuel burning at the optimum rate. Unlike both methanol and ethanol, butanol can also be blended with aviation fuels in limited amounts and its corresponding diester, butyl butyrate, shows good compatibility with aviation kerosene (34). This may be crucial for decarbonisation of the aviation industry as major industrial nations move towards net zero CO2 emissions in the coming decades.

While there are biological routes for the creation of sustainable butanol from carbon dioxide, particularly acetone–butanol–ethanol (ABE) fermentation, separation of low-concentration butanol from water is challenging due to the low volatility of the butanol and the fact that high concentrations of butanol are toxic to microorganisms, limiting the extent of the fermentation for butanol synthesis (35). One method to avoid these issues is to instead dimerise easily manufactured bioethanol via borrowed hydrogen or Guerbet chemistry (36) (see Figure 3).

Fig. 3

Scheme showing borrowed hydrogen/Guerbet condensation of ethanol to produce butanol (higher alcohols can also be produced by further condensation of butanol)

Scheme showing borrowed hydrogen/Guerbet condensation of ethanol to produce butanol (higher alcohols can also be produced by further condensation of butanol)

As with the biological routes above, most potential methods to synthesise butanol from CO2 will similarly involve a multistep process. For example, the Guerbet route could also be appropriate for a CO2 to fuels approach, by first carrying out the conversion of CO2 to ethanol and then using the ethanol as a feedstock for the generation of butanol or other higher alcohols. This can be carried out using conventional transition metal catalysis, with reduction being combined with methylation of the absorbed and partially reduced CO2 to generate the C2 alcohol. The chemical stability of ethanol, a quirk of its structure, allows this process to be carried out under surprisingly mild conditions and with high selectivity. Catalysts that have shown good activity have included palladium-copper nanoparticles and cobalt-alumina catalysts, both have been able to produce ethanol at over 90% selectivity under 200°C, with the palladium-copper nanoparticles achieving production of over 100 mmol ethanol per gram catalyst per hour (37). Interestingly however, the cobalt-alumina catalysts, while less active for ethanol production, showed trace production of butanol directly, suggesting that a direct conversion of CO2 to butanol may be possible with the development of the right catalyst and conditions (38).

CO2-to-ethanol has also been carried out using both atomically divided copper and traditional Cu/ZnO/Al2O3 catalysts, used for methanol synthesis, with electrochemical or plasma assistance. The former has recently been carried out with a Faradaic efficiency of over 90% at −0.7V, although both routes showed very low turnover rates (39, 40). Once again, the fact that butanol has also recently been generated directly from CO2 by copper electrocatalysis in low yield is worthy of note: in this case, it is thought that the acetaldehyde intermediate has undergone in situ condensation, as found in Guerbet chemistry (41).

An alternative method to convert CO2 to butanol, using Grignard chemistry, has been demonstrated by the authors (Figure 4). First methylmagnesium bromide is synthesised, which can be generated by the reaction of methyl bromide, produced from CO2-derived methanol, with magnesium. This then can be reacted with dilute gas phase CO2 at room temperature and atmospheric pressure to generate acetic acid, thus incorporating the CO2 capture process itself into the fuel generation. This acetic acid was then dimerised via Claisen condensation and reduced using copper on zinc oxide and hydrogen to form a mixture of alcohols including butanol. In principle the magnesium halide byproduct could then be recycled by high efficiency electrolysis, also allowing for the creation of further methyl halide and an overall electrosynthesis-by-proxy route (42). The magnesium can be regenerated in existing electrolysis processes and returned to the process, an example of stoichiometric metal looping. As the electrolysis process is routinely used to produce magnesium from sea water, additional magnesium halide in the process will increase the efficiency of the metal production.

Fig. 4

A CO2 to butanol route involving Grignard chemistry (with the Grignard generated from CO2 methanol) and Claisen condensation and subsequent hydrogenation of the Grignard product to produce butanol from CO2 and H2 with all other components regenerated by electrolysis

A CO2 to butanol route involving Grignard chemistry (with the Grignard generated from CO2 methanol) and Claisen condensation and subsequent hydrogenation of the Grignard product to produce butanol from CO2 and H2 with all other components regenerated by electrolysis

As a nascent part of the CO2-to-fuels research field, other routes could yet be discovered. Some of these routes could include a selective MTO process to produce either butenes or ethylene from CO2-derived methanol. After dimerisation (if ethylene is used) the resulting butenes can be simply hydrated to produce (primarily) 2-butanol, which is the main industrial manufacturing method for 2-butanol, and also the preferred butanol isomer for transport fuels (43). Finally, butanol can be synthesised directly from sustainable synthesis gas by Cr/ZnO catalysts, although as might be anticipated, selectivity and yield to butanol by this route has so far been low (44).

Dimethyl Ether and Oxymethylene Ethers

Synthetic transport fuels will be in increasing demand as fossil-based fuels are phased out. The initial focus in this paper has been on methanol, however internal combustion engines need to be modified because of the corrosivity of high concentration methanol fuels (these are generally limited to below 18% of the fuel as a consequence) as discussed previously. Drop-in hydrocarbons such as synthetic diesel and kerosene have been developed, however these are expensive approaches and require considerable quantities of dihydrogen as a major byproduct of the reduction process is water. Recent developments have focused on DME, formed by the condensation of CO2-derived methanol (45). Indeed, Volvo (46) and Ford (47) trucks in North America have developed DME vehicles that have been deployed in commercial environments. DME has a lower energy density than diesel but, unlike lower alcohols, is a direct drop-in fuel at 100% concentration. As it contains no C–C bonds it has much lower (approaching zero) particulate emissions than diesel (5) and as it is not fossil-derived it has no SOx emissions. DME (CH3OCH3) has less hydrogen than diesel (C18H38) and so becomes a more economical proposition as less dihydrogen needs to be produced in order to reduce the CO2. One major challenge will be to produce DME in a single-step process from CO2 and dihydrogen, or preferably water. Photocatalysis may offer a viable route to achieve this sustainably.

In many countries, governments are proposing a transition to electric vehicles (EVs) as a means to defossilise road transport. However, while there are advantages such as zero tailpipe greenhouse gas emissions, there are also many problems. For a true picture of environmental impact, comparative ‘well to wheel’ and ‘weather to wheel’ technologies should be compared and the latter should be based solely on low carbon energy as a changing grid mix will lead to different carbon intensities (48) with the actual emissions being transferred to point source emitters; power stations. Furthermore, we will need fuels that are compatible with existing internal combustion (IC) engines for the foreseeable future if we wish to avoid the risk of creating a social transport underclass; restricting the use of older spark injection (SI) and compression injection (CI) vehicles.

Ford in Aachen, Germany announced the world’s first original equipment manufacturer (OEM)-built DME passenger vehicle, a Ford Mondeo, at the DME Sustainable Mobility Workshop at Landesvertretung NRW in Berlin in 2019 (49). Ford has claimed that the well-to-wheel CO2 emissions for a DME powered CI engine could be as low as 5 g km−1, compared to a conventional diesel fuel value of 116 g km−1 (4). A technoeconomic analysis (TEA) of DME derived from CO2 has shown that DME can be produced at a 740 tonnes per day scale with a minimum selling price of €2193 per tonne, which compares well with fossil-derived DME of around US$3000 per tonne (50).

Conventional DME synthesis relies on the formation of methanol from natural gas or syngas, the latter being an exothermic process as shown in Equation (iii). Direct hydrogenation (Equations (iv) and (v)) can also be achieved catalytically as discussed previously, with the enthalpy of reaction being less than that of CO.


Acid catalysed dehydration in the condensation of two molecules of methanol gives DME in an exothermic reaction (Equation (vi)). In order for this be considered a sustainable process, the methanol should be produced from captured CO2 or from biogenic methanol. Both of these approaches have been applied to the commercial synthesis of DME by Oberon Fuels (51). The provenance of the supply has led to the DME gaining Renewable Fuel Standard approval from the US Environmental Protection Agency.


Recently, considerable effort has been directed to the direct synthesis of DME from captured CO2 and hydrogen (Equation (vii)). The advantages include a single process operation and a highly exothermic reaction. However, there is still an issue that of the six equivalents of hydrogen consumed, half end up in the water byproduct.


It has been shown that DME can be produced by the direct reduction of CO2, however a more exothermic process is the direct hydrogenation of CO in the form of syngas in a 1:1 stoichiometry (Equation (viii)) (52, 53).


A benefit of this process is that all the hydrogen is retained in the DME product, however the byproduct is one equivalent of CO2. There is of course the opportunity to separate the CO2 and feed it into a second reactor to produce more DME using the processes described in the following discussions. This offers an opportunity to utilise waste gases from iron and steel industries which contain high concentrations of CO and CO2 as well as hydrogen in the furnace off-gas (54).

Bifunctional catalysts, such as Cu-In-Zr-O with SAPO-34 zeolite (CIZO-SAPO) have been reported (55) for the direct conversion of CO2 to DME at 250°C and 30 bar. While the selectivity to DME is good (64%) the conversion of CO2 is disappointing at 4.2%.

Polierer et al. (56) have reported a direct synthesis of DME from CO2 using a mixed catalyst system based on Cu/ZnO/ZrO2 produced by continuous precipitation. The catalyst combines methanol synthesis with subsequent dehydration using CO/CO2 mixtures at 230°C and 50 bar. DME synthesis was enhanced when CO2-rich gas feeds were used.

The use of a hybrid Cu/ZnO/ZrO2-ferrite (CZZ(C)-FER) catalyst to produce DME directly from CO2 has been reported (57). A mechanism was proposed in which hydrogen is adsorbed onto the copper atom and CO2 onto the Zn-Zr-FER surface. Formation of formate on the surface is achieved by hydrogen transfer which then undergoes dehydration through further hydrogen transfer to give the surface bound methoxide. Two methoxides then combine to give DME, completing the dehydration step.

Modak et al. (58) have recently reviewed the catalytic reduction of CO2 to give amongst other things methanol and DME and have included the use of hydrides and carbon instead of hydrogen as the reducing agent. An optimised reactor has been used for the direct synthesis of DME from CO2 (59) using CuO/ZnO/Al2O3 and γ-Al2O3 as the catalyst system.

In common with many reports, Kornas et al. (60) have reported the Cu-ZrO2 system as an active catalyst for DME direct synthesis from CO2, modified using a heteropolyacid, montmorillonite K10 as the acidic motif.

The energy density (MJ l−1) of DME is only 54% that of diesel, and 60% of its specific energy (MJ kg−1). However, it also contains significantly less carbon and so when it burns in air or oxygen it follows the following stoichiometric reaction, Equation (ix):


By contrast, the combustion of diesel can be generalised as follows, Equation (x):


It has been shown that despite the lower energy density and specific energy, in a conventional compression engine, DME demonstrates lower well-to-wheel emissions when compared to fossil-oil derived diesel (61).

DME is a gas under ambient conditions so needs to be stored under slightly pressurised conditions (5.1 bar at 20°C), but considerably lower than the pressures required for hydrogen. In the vehicle, the DME must be pressurised to 12–30 bar to ensure the material is in the liquid phase (62). Oxymethylene ethers (OMEx ) may ultimately be a better option as those with more than three carbons (OME1 and higher) are liquids that can be stored in conventional tanks. However, the emissions reductions decrease as the value of x increases as while the density becomes similar to diesel the energy density does not increase proportionately. Furthermore, as x increases so do the production costs.

A one-pot synthesis of OME1 by hydrogenation of CO2 in methanol using a 3% ruthenium catalyst over the high silica zeolite BEA has been reported (63) to give good selectivity at 150°C (Equation (xi)). A mechanistic study also suggests that the reaction proceeds via a bound formate species.



While there is a drive towards electrification of the road transport system, there will still be a need for fuels to power internal combustion engines for the foreseeable future. This is because there will still be legacy vehicles in use if a social underclass is to be avoided and also where high energy density is required, for example in long-distance road haulage. While there has been considerable acceleration in synthetic hydrocarbon production, there is also an emerging market for oxygenated fuels with lower emissions. These include methanol, butanol and methylene ethers such as DME and OMEx . Of these, perhaps the greatest promise is shown for DME due to soot emissions approaching zero and reduced well-to-wheel CO2 emissions even when compared to EVs depending on the source of the electricity. The challenge lies in the synthesis of methylene ethers through selective oligomerisation (64) and directly for CO2 using mild reaction conditions and catalysts based on sustainable elements, such as iron, nickel and copper. There also needs to be policy interventions to aid the transition from fossil-based fuels to synthetic carbon-based fuels while servicing existing engine architectures until a new vehicle norm is established.

The challenge is truly interdisciplinary taking expertise from chemistry, engineering and the social sciences. The transition will also need sustainable finance in order to accelerate deployment. However, perhaps the greatest need is for a high level of creative thinking to allow paradigm shifts in technology rather than slow incremental development. Whatever happens, catalysis will be at the centre of these activities.

A range of methodologies have been discussed for the production of oxygenated synthetic transport fuels. Each is at a different level of maturity or technology readiness level (TRL). These range from the synthesis of butanol from Grignard agents (TRL3) to the commercial production of DME (TRL9) which is being deployed at scale through a recent marketing opportunity between Oberon Fuels and Suburban Propane in the USA. It is important that the environmental sustainability of the new materials is fully evaluated using robust and open life cycle assessment (LCA), however this should be carried out in the context of TEA so that the commercial viability of the process is also considered. Readers are therefore recommended to consider recent publications that highlight the need for harmonisation of such approaches with respect to carbon dioxide utilisation technologies (50, 56, 65, 66).



  1. 1.
    P. Styring, E. A. Quadrelli and K. Armstrong, “Carbon Dioxide Utilisation: Closing the Carbon Cycle”, Elsevier, Amsterdam, The Netherlands, 2015 LINK
  2. 2.
    J. Priestley, “Directions for Impregnating Water with Fixed Air: In Order to Communicate to it the Peculiar Spirit and Virtues of Pyrmont Water, and Other Mineral Waters of a Similar Nature”, J. Johnson, London, UK, 1772 LINK
  3. 3.
    P. M. Maitlis and A. de Klerk, “Greener Fischer-Tropsch Processes: For Fuels and Feedstocks”, Wiley, Weinheim, Germany, 2013 LINK
  4. 4.
    “Sustainable Synthetic Carbon Based Fuels for Transport: Policy Briefing”, The Royal Society, London, UK, September, 2019 LINK
  5. 5.
    W. Willems, ‘Sustainable Fuels for Future Mobility: The DME Opportunity for CI-Engines’, 8th International DME Conference, Sacramento, CA, USA, 10th–12th September, 2018
  6. 6.
    ‘Fossil and Alternative Fuels - Energy Content’, The Engineering Toolbox, 2008 LINK
  7. 7.
    ‘Fuels - Higher and Lower Calorific Values’, The Engineering Toolbox, 2003 LINK
  8. 8.
    M. C. Molstad and B. F. Dodge, Ind. Eng. Chem., 1935, 27, (2), 134 LINK
  9. 9.
    G. A. Olah, Angew. Chem. Int. Ed., 2013, 52, 1, 104 LINK
  10. 10.
    C. Hobson and C. Márquez, “Renewable Methanol Report”, Methanol Institute, Singapore, December, 2018 LINK
  11. 11.
    K. Larmier, W.-C. Liao, S. Tada, E. Lam, R. Verel, A. Bansode, A. Urakawa, A. Comas-Vives and C. Copéret, Angew. Chem. Int. Ed., 2017, 56, (9), 2318 LINK
  12. 12.
    V. D. B. C. Dasireddy and B. Likozar, Renew. Energy, 2019, 140, 452 LINK
  13. 13.
    M. Behrens, F. Studt, I. Kasatkin, S. Kühl, M. Hävecker, F. Abild-Pedersen, S. Zander, F. Girgsdies, P. Kurr, B.-L. Kniep, M. Tovar, R. W. Fischer, J. K. Nørskov and R. Schlögl, Science, 2012, 336, (6083), 893 LINK
  14. 14.
    M. Huš, V. D. B. C. Dasireddy, N. S. Štefaničič and B. Likozar, Appl. Catal. B: Environ., 2017, 207, 267 LINK
  15. 15.
    J. T. Sun, I. S. Metcalfe and M. Sahibzada, Ind. Eng. Chem. Res., 1999, 38, (10), 3868 LINK
  16. 16.
    A. Prašnikar, A. Pavlišič, F. Ruiz-Zepeda, J. Kovač and B. Likozar, Ind. Eng. Chem. Res., 2019, 58, (29), 13021 LINK
  17. 17.
    X. Wei, Z. Yin, K. Lyu, Z. Li, J. Gong, G. Wang, L. Xiao, J. Lu and L. Zhuang, ACS Catal., 2020, 10, (7), 4103 LINK
  18. 18.
    W. Zhou, K. Cheng, J. Kang, C. Zhou, V. Subramanian, Q. Zhang and Y. Wang, Chem. Soc. Rev., 2019, 48, (12), 3193 LINK
  19. 19.
    W. Wang, S. Wang, X. Ma and J. Gong, Chem. Soc. Rev., 2011, 40, (7), 3703 LINK
  20. 20.
    J. Díez-Ramírez, P. Sánchez, A. Rodríguez-Gómez, J. L. Valverde and F. Dorado, Ind. Eng. Chem. Res., 2016, 55, (12), 3556 LINK
  21. 21.
    T. Toyao, S. Kayamori, Z. Maeno, S. M. A. H. Siddiki and K.-i. Shimizu, ACS. Catal., 2019, 9, (9), 8187 LINK
  22. 22.
    X. Jiang, N. Koizumi, X. Guo and C. Song, Appl. Catal. B: Environ., 2015, 170-171, 173 LINK
  23. 23.
    S. Dang, H. Yang, P. Gao, H. Wang, X. Li, W. Wei and Y. Sun, Catal. Today, 2019, 330, 61 LINK
  24. 24.
    S. Xiao, Y. Zhang, P. Gao, L. Zhong, X. Li, Z. Zhang, H. Wang, W. Wei and Y. Sun, Catal. Today, 2017, 281, (2), 327 LINK
  25. 25.
    O.-S. Joo, K.-D. Jung, I. Moon, A. Ya. Rozovskii, G. I. Lin, S.-H. Han and S.-J. Uhm, Ind. Eng. Chem. Res . 1999, 38, (5), 1808 LINK
  26. 26.
    J. Toyir, R. Miloua, N. E. Elkandri, M. Nawdali, H. Toufik, F. Miloua and M. Saito, Phys. Proc., 2009, 2, (3), 1075 LINK
  27. 27.
    G. Dolan, ‘Methanol: Emerging Global Energy Markets’, 16th Annual State of the Energy Industry Forum, Washington, DC, USA, 23rd January, 2020
  28. 28.
    X. Su, X. Yang, B. Zhao and Y. Huang, J. Energy Chem., 2017, 26, (5), 854 LINK
  29. 29.
    P. Lahijani, Z. A. Zainal, M. Mohammadi and A. R. Mohamed, Renew. Sust. Energy Rev., 2015, 41, 615 LINK
  30. 30.
    F.-Y. Gao, R.-C. Bao, M.-R. Gao and S.-H. Yu, J. Mater. Chem. A, 2020, 8, (31), 15458 LINK
  31. 31.
    G. Chen, L. Wang, T. Godfroid, and R. Snyders, ‘Progress in Plasma-Assisted Catalysis for Carbon Dioxide Reduction’, in “Plasma Chemistry and Gas Conversion”, eds. N. Britun and T. Silva, IntechOpen, London, UK, 2018, pp. 59–69 LINK
  32. 32.
    D. Ramey and S.-T. Yang, ‘Production of Butyric acid and Butanol from Biomass’, US Department of Energy, Oak Ridge, TN, USA, 2005 LINK
  33. 33.
    S. Szwaja and J. D. Naber, Fuel, 2010, 89, (7), 1573 LINK
  34. 34.
    R. W. Jenkins, M. Munro, S. Nash and C. J. Chuck, Fuel, 2013, 103, 593 LINK
  35. 35.
    B. O. Abo, M. Gao, Y. Wang, C. Wu, Q. Wang and H. Ma, Environ. Sci. Poll. Res., 2019, 26, 20164 LINK
  36. 36.
    H. Aitchison, R. L. Wingad and D. F. Wass, ACS Catal., 2016, 6, (10), 7125 LINK
  37. 37.
    S. Bai, Q. Shao, P. Wang, Q. Dai, X. Wang and X. Huang, J. Am. Chem. Soc., 2017, 139, (20), 6827 LINK
  38. 38.
    L. Wang, L. Wang, J. Zhang, X. Liu, H. Wang, W. Zhang, Q. Yang, J. Ma, X. Dong, S. J. Yoo, J.-G. Kim, X. Meng and F.-S. Xiao, Angew. Chem. Int. Ed., 2018, 57, (21), 6104 LINK
  39. 39.
    H. Xu, D. Rebollar, H. He, L. Chong, Y. Liu, C. Liu, C.-J. Sun, T. Li, J. V. Muntean, R. E. Winans, D.-J. Liu and T. Xu, Nat. Energy, 2020, 5, 623 LINK
  40. 40.
    B. Zhao, Y. Liu, Z. Zhu, H. Guo and X. Ma, J. CO2 Util., 2018, 24, 34 LINK
  41. 41.
    L. R. L. Ting, R. García-Muelas, A. J. Martín, F. L. P. Veenstra, S. T.-J. Chen, Y. Peng, E. Y. X. Per, S. Pablo-García, N. López, J. Pérez-Ramírez and B. S. Yeo, Angew. Chem. Int. Ed., 2020, 59, (47), 21072 LINK
  42. 42.
    G. R. M. Dowson and P. Styring, Front. Energy Res., 2017, 5, 26 LINK
  43. 43.
    F. Speiser, P. Braunstein and L. Saussine, Acc. Chem. Res., 2005, 38, (10), 784 LINK
  44. 44.
    L. Tan, G. Yang, Y. Yoneyama, Y. Kou, Y. Tan, T. Vitidsant and N. Tsubaki, Appl. Catal. A: Gen., 2015, 505, 141 LINK
  45. 45.
    M. Y. Kim, S. H. Yoon, B. W. Ryu and C. S. Lee, Fuel, 2008, 87, (12), 2779 LINK
  46. 46.
    ‘Mack Trucks Tests Alternative Fuel DME’, Volvo Group, Gothenburg, Sweden, 24th January, 2017 LINK
  47. 47.
    ‘Ford Leads Project to Develop Near Zero Particulate Emission Diesel Cars that Could Run On Converted CO2’, Ford of Europe, Aachen, Germany, 11th September, 2015 LINK
  48. 48.
    J. McLaren, J. Miller, E. O’Shaughnessy, E. Wood and E. Shapiro, ‘Emissions Associated with Electric Vehicle Charging: Impact of Electricity Generation Mix, Charging Infrastructure Availability, and Vehicle Type’, NREL/TP-6A20-64852, National Renewable Energy Laboratory, Golden, CO, USA, April, 2016 LINK
  49. 49.
    Thangavelu Jayabalan, ‘Flexible DME Production From Biomass: Fledged Project Update’, DME Sustainable Mobility Workshop, Berlin, Germany, 24th May 2019 LINK
  50. 50.
    S. Michailos, S. McCord, V. Sick, G. Stokes and P. Styring, Energy Conv. Manage., 2019, 184, 262 LINK
  51. 51.
    A. Corradini and J. McCormick, Oberon Fuels Inc, ‘Process and System for Converting Biogas to Liquid Fuels’, US Patent 8809603; 2014
  52. 52.
    M. Aresta and A. Dibenedetto, Dalton Trans., 2007, (28), 2975 LINK
  53. 53.
    C.-H. Huang and C.-S. Tan, Aerosol Air Qual. Res., 2014, 14, (2), 480 LINK
  54. 54.
    J. Schittkowski, H. Ruland, D. Laudenschleger, K. Girod, K. Kähler, S. Kaluza, M. Muhler and R. Schlögl, Chem. Ing. Techn., 2018, 90, (10), 1419 LINK
  55. 55.
    L. Yao, X. Shen, Y. Pan and Z. Peng, Energy Fuels, 2020, 34, (7), 8635 LINK
  56. 56.
    S. Polierer, D. Guse, S. Wild, K. H. Delgado, T. N. Otto, T. A. Zevaco, M. Kind, J. Sauer, F. Studt and S. Pitter, Catalysts, 2020, 10, (8), 816 LINK
  57. 57.
    Q. Sheng, R.-P. Ye, W. Gong, X. Shi, B. Xu, M. Argyle, H. Adidharma and M. Fan, J. Environ. Sci., 2020, 92, 106 LINK
  58. 58.
    A. Modak, P. Bhanja, S. Dutta, B. Chowdhury and A. Bhaumik, Green Chem., 2020, 22, (13), 4002 LINK
  59. 59.
    N. D. Otalvaro, M. Kaiser, K. H. Delgado, S. Wild, J. Sauer and H. Freund, React. Chem. Eng., 2020, 5, (5), 949 LINK
  60. 60.
    A. Kornas, M. Śliwa, M. Ruggiero-Mikołajczyk, K. Samson, J. Podobiński, R. Karcz, D. Duraczyńska, D. Rutkowska-Zbik and R. Grabowski, React. Kinet. Mech. Catal., 2020, 130, 179 LINK
  61. 61.
    U. Lee, J. Han, M. Wang, J. Ward, E. Hicks, D. Goodwin, R. Boudreaux, P. Hanarp, H. Salsing, P. Desai, E. Varenne, P. Klintbom, W. Willems, S. L. Winkler, H. Maas, R. De Kleine, J. Hansen, T. Shim and E. Furusjö, SAE Int. J. Fuels Lubr., 2016, 9, (3), 546 LINK
  62. 62.
    S. Hänggi, P. Elbert, T. Bütler, U. Cabalzar, S. Teske, C. Bach and C. Onder, Energy Rep., 2019, 5, 555 LINK
  63. 63.
    W. Ahmad, F. L. Chan, A. Hoadley, H. Wang and A. Tanksale, Appl. Catal. B: Environ., 2020, 269, 118765 LINK
  64. 64.
    C. H. Gierlich, K. Beydoun, J. Klankermayer and R. Palkovits, Chem. Ing. Techn., 2020, 92, (1–2), 116 LINK
  65. 65.
    A. W. Zimmermann, J. Wunderlich, L. Müller, G. A. Buchner, A. Marxen, S. Michailos, K. Armstrong, H. Naims, S. McCord, P. Styring, V. Sick and R. Schomäcker, Front. Energy Res., 2020, 8, 5 LINK
  66. 66.
    V. Sick, K. Armstrong, G. Cooney, L. Cremonese, A. Eggleston, G. Faber, G. Hackett, A. Kätelhön, G. Keoleian, J. Marano, J. Marriott, S. McCord, S. A. Miller, M. Mutchek, B. Olfe-Kräutlein, D. Ravikumar, L. K. Roper, J. Schaidle, T. Skone, L. Smith, T. Strunge, P. Styring, L. Tao, S. Völker and A. Zimmermann, Energy Technol., 2019, 8, (11), 1901034 LINK


We thank the UKRI Engineering and Physical Sciences Research Council (EPSRC) for funding under the SUSTAIN Manufacturing Hub (EP/S018107/1) for funding to George Dowson.

Supplementary Information

Oberon Fuels LINK

International DME Association, Industry Events LINK

The Authors

Peter Styring is Professor of Chemical Engineering & Chemistry at The University of Sheffield, UK. He is a former Head of the Chemistry Department. His expertise lies in carbon dioxide capture and utilisation with particular interests in catalysis and the production of low-carbon synthetic transport fuels and fertilisers.

George Dowson is a Postdoctoral Research Associate in the Styring Group at The University of Sheffield. His expertise lies in catalysis, novel carbon capture approaches and creation of sustainable synthetic fuels.

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