Robert
Schlögl
ab
aMax-Planck-Institut for Chemical Energy Conversion, Stiftstr. 34–36, 45470 Mülheim an der Ruhr, Germany
bFritz Haber Institute of the Max Planck Society, Faradayweg 4–6, 14195 Berlin, Germany
First published on 18th February 2021
The quest for the sustainable energy transition requires replacing fossil fuels by renewable electricity (RE). Systems of energy supply consist of both electrons and molecules as energy carriers. It is thus essential to interconvert both types of carriers. Capitalizing on the intrinsic efficiency of using electrons it is desirable to electrify in the sustainable system more end energy applications than in the fossil system being fully based upon molecular carriers. This does not eliminate the need to retain molecules as energy carriers in a substantial fraction of a whole energy system. The application “energy storage” as example compensates the volatility of RE and is thus critical to any energy transition. Chemical energy conversion (CEC) is the critical science and technology to eliminate fossil fuels, to create circular energy economies and to enable global exchange of RE. This paper describes generic structural features and dimensions of CEC.
Another consequence is that the primary source of energy in the future will be RE. This energy is local (within the range of a power transmission grid) and volatile (incompatible with baseload requirements). It can (in contrast to the present situation) only be traded inside its grid and cannot be distributed globally and it needs to be used at the instant of its generation. This is in strong contrast2 to the quest for a demand-driven secure supply. At present in Europe up to half of the average electrical load can be supplied by volatile RE supplemented by the other half from fossil and nuclear sources. Fig. 1 gives an illustration of the complexity of the power sector of the actual German electrical grid. The absence of a baseload structure is evident as is the critical function of import-export substituting national energy storage capacities of relevant dimensions.
On a higher integrated scale, it is not easy to see that more RE in an electrical grid will automatically reduce the CO2 emission. Fig. 2 illustrates this for Germany. The steady increase in RE fraction is not mirrored by a steady reduction of CO2 emission. Variable power consumption and fluctuations in the primary energy mix both strongly affected by economic boundary conditions are made responsible for this effect. The figure reveals that an energy transformation based upon subsidised influx of RE alone will not automatically defossilize the power system nor will it transform the system into a sustainable future.
Fig. 2 Fractions of RE in the German power system (green) and change in power-related CO2 emissions (red). The absolute CO2 emission in 2002 was 372 Mt. |
The span of volatility in the power generation that has reached in Germany now about 80% of the average load (Fig. 1) indicates a technical hindrance in removing conventional power generation. The economics of these critically required installations are compromised by the rapid reduction in full load hours leading to severe conflicts with neighbouring electricity grids by import/export as well as in the regulatory and economic system. Recognizing the need to provide synthetic fuels to the combustion power industry would not only remove much of the conflict potential but could speed up the defossilization of the power sector. The important role of natural gas as an intermediate solution is not seen clearly enough by stakeholders and might soon be compromised by the emerging trend to refurbish the gas transmission system into a hydrogen transport system. These phenomena urgently call for a roadmap with a realistic timeline to avoid conflicts between energy sectors that prevent a fast and economically viable transformation of the fossil energy system with its infrastructures.
The situation is complicated by the unclear definition of “sustainable energy system”. Some assume that nuclear fission options are part of the trajectory whereas others do not. Others accept the pyrolysis of fossil fuels into the chemical elements hydrogen and carbon as a contribution to the transformation, despite of the finite nature of this resource. Yet others include carbon capture and storage (CCS) as emission reduction option that is opposed by many including much of the broader public.
Only few countries besides those who rely on hydroelectricity as non-volatile RE have reached 50% RE content in their electrical grids and begin to run into the challenge of maintaining supply security while continuing de-fossilization. Fig. 1 gives an illustration that the German power system could not maintain stability without a European exchange. This is not a speciality of the German system but can also be observed in other European systems. In Fig. 3 the situation of Germany is compared to that existing in Denmark. This example was chosen as it has one of the highest fractions of RES in its electricity supply. The fuels for electricity generation besides wind and solar are largely biomass-based. The data are aggregated for the first 8 month of the year 2020. The interpretation of the data from Germany is intricate as such a large system has many influences affecting the trends. The example Denmark is much smaller and relates to a more homogeneous use case allowing for detecting some clear trends. In both graphs the effect of the corona pandemic with the drop in month April is detectable when comparing the trend data to the year 2019 (not shown here).
It is obvious that Germany has reached an enormous penetration of RE into its electricity system. Surprising is the high penetration for the small country of Denmark as is the fact that its use of wind (and solar) is less than expected. In both cases the system of imports and exports is used to maintain grid stability. The multiplicity of primary energy sources in both cases leads to instability patterns being compensated on short and medium timescales by a combination of import and export simultaneously. It is worth to notice that both countries have decided to act as net exporters of electricity. The motivation for this activity is expected to be very different in view of the availability of primary energy carriers in both countries. In short, the system of import/export options within Europe is absolutely critical to guarantee the stability of electrical supplies also with high fractions of volatile RE. No serious measures of energy storage besides smoothing short fluctuations buffered by electro-mechanical devices are needed as yet. This strategy relies on the cooperation of all countries interconnected and on the wide span of RE penetration into these grids (see e.g. France with high fraction of base load nuclear (Fig. 5) or Poland with high base load of coal). As the RE penetration gets larger in the high RE countries, the need for exchange gets rapidly much larger and eventually interferes with RE expansion in other countries. The only reliable countermeasure is chemical energy conversion in grid scales that is presently considered as not necessary as it is expensive and inefficient. The arguments here show that chemical technologies in energy storage will be needed in the longer run to allow eventually a deep defossilisation of the European energy systems and in this way to make the Green Deal. In addition, no country has started to use bulk amounts of RE in traditional non-electrical sectors of their energy systems that are together larger than the power sector. This “sector coupling” cannot happen without converting RE into chemical energy carriers.
Much of the discussion about energy transformation revolves around defossilizing the power sector by RE and a component for flexibilization being either gas power stations or nuclear fission or biomass combustion or a combination thereof. In such scenarios the storage of RE is of secondary relevance. Batteries are used as short-term buffers and pumped hydro installations as day-to-day storage options. The need for bulk amounts of RE for CEC conversion is negated on grounds of inefficiency and high specific cost of electricity generated from fuels made through CEC. This option is only advertised when high values of above 80% defossilization3 of the power sector are considered.
There is quite a reluctance to accept that CEC or energy storage4 is a relevant option besides carbon capture and storage (CCS). The origins of this conjecture are general efficiency arguments and the diffuse idea that sustainable energy systems should be largely electrical with a residue of below 30% molecular energy storage stemming predominantly from biomass and fossil sources. Efficiency is indeed a highly important factor when the dimension of energy systems is considered. It is however the efficiency of an element (technology) for the functioning of the whole system that counts most. Chemical energy conversion is indispensable for storage and transportation of RE across the whole system. It is thus the systemic efficiency across all services of energy that must be judged for an energy system and not only the process efficiency that is inevitably reduced when more conversion steps are necessary for reaching a certain function. The process efficiency is in competition to the path dependence of a technology: if a given task can be reached with low path dependence (no new infrastructure or large additional investments) a reduced process efficiency may be acceptable at least as transitory step in the multi-decade transformation of an energy system. These aspects reduce the relevance of the fact that round trip efficiencies of RE via chemical fuels for power generation or mobility are at the order of 20% of the initial RE.
It is argued that chemical energy storage and the relevance of chemical research into these issues are of minor relevance and contribute only niche solutions to the sustainable energy systems. The needs of the material-based industries5 (steel, cement, glass, chemicals) are not considered in such views at all on grounds of their relatively small contribution to the size of the energy system. If there is a role for CEC, then electrochemical storage through the HCl electrolysis/synthesis are considered, for efficiency arguments6 plain water splitting into hydrogen and oxygen is less favoured. This process, that powers the energy cycle of nature, will in the author’s view have to play a decisive role in generating the hydrogen needed for technical energy systems. There are other options such as dehydrogenation of hydrocarbon molecules (ΔG0 70 kJ mol−1 for methane) and biological synthesis pathways which may play some role in the future but cannot replace the energy-intense (ΔG0 286 kJ mol−1) water splitting through electrolysis or photo(electro)chemical activation.
A generic scheme of such an energy system is shown in Fig. 4. It is noted that Germany did start with its “Energiewende” in this concept and realizes only now that this may be inadequate with respect to the enormous additional installations of solar and wind devices required.
Fig. 4 A generic energy scheme with minimal energy storage. Blue lines indicate immediate use of RE, red lines use storage options for compensating volatility. |
The elements “chemicals” and “unavoidable CO2 emissions” (e.g. cement, lime) remain outside of the system.
Fig. 5 illustrates for Germany and France, two countries with similar sizes but different structures of their energy systems, how far the transformation was progressing over the last 15 years. Two of the large economies in Europe show a surprisingly parallel evolution of their energy consumption although their economic activities differ significantly. For France there was little change in RE penetration owing to its high fraction of nuclear fission energy. In Germany some reduction of primary energy consumption and a substantial growth of the RE supply mainly as electricity resulted in a significant transformation of the system without, however, reducing the total energy consumption. Some sizeable contributions to the renewable fraction like biomass and hydro-electricity cannot be scaled further. The burden on the solar and wind contributions thus will become larger for reaching the climate targets set in the Green Deal. In addition, as RE is increasing, the volatility challenge increases with the need to enter into the molecular storage regime that is much less energy-efficient than the direct use of RE with its low conversion losses. This factor substantially increases the demand for primary energy even further. It becomes clear that some significant additional element has to be brought into action if the target of carbon neutrality shall be reached within the next 3 decades.
Fig. 5 Consumption of primary energy for two European countries (DE, FR) (red) and fractions of RE thereof (green). (Source EU energy statistics country data sheets edition 2019.) |
This additional element is the global exchange of RE. It is one critical task of CEC to convert free electrons in molecules7 that are sufficiently similar to fossil oil and gas in order to provide the technological option for the continuation of using the infrastructure and application devices existing today. The main function of synthetic fuels and CEC is to make RE into a global commodity that can be exchanged in bulk amounts between areas of excess RE and highly demanding regions with limited local production capacity. Transport of RE in molecules rather than in free electrons is effective8 and can use existing pipeline/shipping infrastructures that are operating today on fossil energy carriers.
Self-sufficiency within the reach of a transmission grid system is the basic concept of energy systems based upon RE only as indicated in Fig. 4. The electrification of energy applications through RE carries substantial advantages in efficiency as the conversion losses between primary energy fuels and end energy (today about 37% in Europe) disappear and reduce the size of the energy system by that number. In areas of the world where the energy system infrastructure is still growing or needs re-design, the “all-electrical” option is a distinct possibility. A pre-requisite is the availability of storage and flexibility options in these energy systems compensating the volatility of RE. Such compensation is possible with CEC (as water splitting to hydrogen and its re-conversion into electricity). See Fig. 4 for a generic layout of such a system.
If, however, part of the energy system is already in molecular carriers it is hard to understand why applications that operate facile with molecular carriers should be electrified enhancing the burden on the electrical system. The faster and less expensive path is to consider energy transformations using as much as possible the elements of the existing energy system and replace the fossil primary energy sources by sustainable ones. Then a global trade of molecular energy carriers made from RE is mandatory. Local RE is an additive and stabilizing factor in a given energy system but the majority of its needs will come from global trading. Energy storage disappears as a major issue in this view and merges into the challenge to convert large amounts (up to 80% of the global RE demand) into sustainable fuels. Fig. 6 illustrates such a generic mixed local-remote9 energy system.
Fig. 6 A generic energy system with global exchange of RE. The black lines indicate how carbon for synthetic fuels is fed into the chemical energy conversion processes (CEC) without using fossil carbon sources. “Deposition” stands for formation and storage of solid carbon (or minerals) for long-term immobilization of carbon under full control. All essential elements of the system are now interconnected (compare to Fig. 4). |
The RE is generated at spots on the planet where maximum capacity factors of combined wind and PV installations can be expected.8 Capacity factors of 0.5 and above are possible in extreme locations where human life is difficult. The combined capacity factor for Germany is 0.17, within Europe values up to 0.35 have been observed. Please note that these values are not constant but vary with time and exact location as both climate and weather are determining factors. At the highly productive locations RE is converted first to hydrogen and then to a transport form of a synthetic fuel10 allowing global trading. In this way fossil oil and gas are replaced by renewable oil and gas or as stated by “green oil and green gas”.8,11 Examples of such fuels are synthetic diesel, “C1 fuels”, ammonia, synthetic methane, LOHC or methanol.12 Particular attention is needed for the mobility sector where synthetic fuels create “leaks” of significant dimensions in the circular use of carbon. They may be acceptable for some time in which fossil fuels are replaced by synthetic ones but must not be “removed” by double counting13 of CO2 utilization. Eventually they need closure with measures exemplified in Fig. 6. The data in Tables 2 and 3 support the delayed attention to this issue with respect to priorities in other energy sectors.
The local RE generation will be supported by CEC14 as a flexibility measure in limited scales depending on the local capacity factor and on the extent of RE penetration into the energy system. Viewing the development from the target of maximal defossilization it may be expected that in Germany up to 20% of the RE production is used for chemical energy conversion, mainly for hydrogen production.3 A good number for the dimension is 10 GW electrolysis capacity in Germany. It must be stated that this is by no means the demand in chemical energy fuels but rather indicates the contribution for local (national) generation. Energy storage is effectively also performed as mechanical and thermal storage15 that will, however, not be considered here despite its clear technological and cost advantages, as they are always local and of limited volume compared to the potential of global RE exchange.
It occurs that the initiated energy transition with installing local RE systems16 and gradually decommissioning fossil power plants is one part of the solution. The concept of remote RE and its CEC7 followed by transport and utilization in densely populated areas is the critical second part of trajectories into sustainable systems. It is fair to say that energy storage into “green fuels”17 represents an indispensable component for sustainable energy systems. It is not a final small addition as thought earlier but it is likely to carry a main fraction of the burden in defossilization. It is prerequisite that the primary converters of sunlight into RE (PV, CSP, wind) keep developing in scale18 and reliability as in the past. The announcement of much more effective PV systems19 in combination with converters enhancing the capacity factor coming into scalable application12a,20 within this decade allows expecting that the conversion of RE into hydrogen will be able in suitably large dimensions at cost competitive for a global energy exchange.
Estimating the price of green gas is difficult as the technology in the form of a working supply chain does not exist yet in any scaled dimension. The critical regulatory framework determining to a large extent the final price of energy is also not existing yet. Hence the cost estimates are rather theoretical. The fact that the world and in a leading role Europe have decided to go ahead with the RE approach for defossilization makes discussion about this point less relevant: one is in search for the most cost-effective way to bring large amounts of chemically stored RE into a global trade and exchange situation. The extra cost for this is within the dimension of the difference between cost and price for the current energy carriers. The price of RE within the scalable scheme indicated in Fig. 6 for the energy user is to a large extent dependent on non-technical factors. Science and technology can reduce within limits the cost by optimizing the scalable technologies for the interconversion processes that require all interfacial chemical transformations driven by renewable heat or renewable electricity.
The most general estimate is that green fuels replace fossil fuels with the equivalent final energy content. If one takes the energy equivalent of the global oil and global gas industry one gets an impression about dimensions. Relevant numbers for the world energy system of 2017 are taken from the BP world energy statistics and collected in Table 1.
Energy carrier | Value (TWh) |
---|---|
Total primary energy | 156702 |
- Oil | 53579 |
- Coal | 43240 |
- Gas | 36541 |
- Hydropower | 10700 |
- Nuclear | 6943 |
- RES | 5699 |
The fraction of RE from biomass wind and sun is with roughly 3% still small when the target of complete elimination of fossil energy within 3 decades is considered. The situation in different parts of the world is quite different with respect to the dynamics of share of energy carriers and total consumption. In Asia the dynamics is enormous whereas in EU (28) the evolution is rather static. In Table 2 the breakdown of primary energy use is shown for Europe representing 13% of the global primary energy system.
Energy use | Total (TWh) | Fraction thereof (TWh) | Fraction thereof (TWh) | Relative (%) |
---|---|---|---|---|
Total primary | 19992 | 100 | ||
Final energy | 12328 | 62 | ||
Heat | 5394 | 27 | ||
Mobility | 3640 | 18 | ||
- Road | 3559 | |||
Power | 3294 | 16 | ||
- Fossil | 1397 | 7 | ||
- RES | 1006 | 5 | ||
- Nuclear | 830 | 4 |
In order to develop an impression of the dimensions of green energy storage the following quantitative framework shall be used. A circular economy of carbon is assumed to be based upon the couple of methanol22 combustion and CO2 hydrogenation with electrolytic water splitting all based upon RE. Existing technologies23 allow to produce MeOH with an energy investment of 10 MW he t−1. The heating value of this MeOH is 5.5 MW hth t−1. In a modern power installation without waste heat use 2.2 MW he t−1 are recovered. An average efficiency loss of 80% for a cycle RE-CEC-RE is a plausible figure for dimensional estimates. From these numbers it follows that storage of 1 TWh electrical energy require 450 kt of MeOH for which one has to invest 4.5 TWhe in RE. The units in Tables 1 and 2 multiplied by 0.5 give the number of megatons (or world scale plants) of methanol synthesis required to store the respective amounts of energy.
In the following a crude estimate will be given about the energy storage demand for Europe using the framework data from Table 2. The largest fraction of the system are conversion losses with 38% of the primary energy consumption. Hence the expectation to reduce the size of the energy system by electrification is well understandable. The volatility of RE requires, however, a massive effort24 in energy storage if carbon neutrality is required and if no nuclear energy is added to the energy mix.25 The estimation discriminates RE generated locally from remote RE requiring transportation as chemical energy carrier. Long term storage (more than 1 day) and backup power as well as the demand of the energy system for molecular energy carriers (“solar” or synthetic fuels”) are assumed to be provided by converting remote RE into shippable energy carriers and transporting them to Europe. There it will be converted into hydrogen and used to cover the need of final energy that cannot be covered locally within Europe. The RE supply is not discriminated into storable (hydroelectric and biomass) and non-storable (solar, wind) forms in order not to further complicate the estimate. Table 3 presents a dimensional framework. This is not intended to replace any scenario of which many sophisticated versions exist. The sole purpose is to deliver an impression about the amounts of energy storage involved in a deep defossilization of the European energy system.
From line 2 it is seen that for power and mobility no net savings are assumed whereas the heat consumption is to drop substantially by building improvements. Smaller savings by efficiency gains are assumed to be compensated by moderately higher demands within the next 3 decades. The fractions of local RE from line 3 include all forms of RE and short-term storage idealized without losses. From lines 5 and 6 it is seen that electrification of mobility earns a massive reduction in energy demand. Line 6 adds up to 3465 TWh European final RE that is needed to support the assumptions about imports detailed below. This is about 3 times more RE than Europe produces today and should thus be an achievable number if all conversion potentials are used. Some countries have reached their potential whereas others have barely started to generate RE and the potential to exchange RE between countries is still rather limited.
A total of 5740 TWh RE as hydrogen has to be imported (line 7, Table 3) to balance the energy needs of Europe. In line 8 substantial efficiency losses are indicated for burning hydrogen in power stations and from converting CO2 into synthetic fuels assumed as methanol. These losses are still idealized as no process energy and transport losses are included. From line 9 the gross hydrogen to arrive in Europe amounts to 7689 TWh. This number can be significantly reduced15 if selected energy saving technologies (line 10) are implemented within whole Europe. Line 12 highlights the enormous savings with only 3752 TWh being required. The by far largest effect has the electrification of all mobility with half of it as battery-electric and the other half of it as serial hybrid powertrains to be used mainly in heavy duty applications. The other large saving arises from the use of heat pumps for house heating purposes with the extra benefit of removing many small emission sources from otherwise gas heating installations.
This still large number does not contain any provision to remove fossil carbon from the material industry (chemicals, cement, lime, steel). These requirements are difficult to be estimated as none of the potential replacement technologies are existing at scale. It is safe to assume that this sector will require RE in the same dimension as all requirements given in Table 3. The frequent attitude to exclude these issues from the scenarios by assuming moving these industries outside of the unit of analysis is not useful in terms of the general intention to minimize the climate change on the planet.
This dimensional framework is crude and may be debatable in many points. It remains, however, that massive efforts are needed to deepen the domestic penetration of RE in Europe and in parallel engage in partnerships to utilize abundant RE reserves in remote areas of the world. It further occurs that efficiency gains projected in many sectorial scenarios are compensated by the losses arising from the need to generate molecular storage species. Nonetheless, there is a good chance that the whole energy system may become smaller without losing any of its functions by the efficiency gains from partial electrification. The projections are subject to the stability of the present fundamental economic and societal boundary conditions. They may change in the coming 3 decades by e.g. less available biomass due to increasing aridity and loss of biodiversity, changes in the global distribution of value chains due to changes in the globalization pattern or the need for more resilience with more regional value generation or climate change-induced waves of migration or changes in energy supply policies following local disasters. Such changes in the trend patters of culture and society cannot be built into projections of the evolution of energy systems and require flexible responses despite the enormous dimensions of infrastructures involved. In addition, the energy supply demands cannot be pre-planned and should be flexible enough to enable societal evolutions. Resilient energy supply strategies are needed offering maximal flexibility against eco-political threats and providing the energy forms needed for the societal evolution. These strategies are based upon a co-existence of electrical RE for direct use within a European grid structure, a storage strategy for short-term fluctuations and an import strategy for long term supply of RE stored in26 hydrogen and its derivatives. In such a setting for sustainable energy supply presently used or considered, non-sustainable elements can be avoided such as fossil fuels, nuclear fission, CCS or extensive use of biomass and the loss of ecosystems stabilizing the biosphere by deforestation or excessive hydroelectric installations.
The broad portfolio of storage options discussed and required for the intended resilient sustainable energy system carries with it several negative effects. The sheer size of the infrastructures needed (like the electricity and the petrochemical industries combined) adds significantly to the land use for energy that is already large for the RE conversion devices (wind mills and solar panels). A rarely discussed aspect is safety of the infrastructure. The pure technical safety (accidents, spills, fires and explosions with chemical storage materials) is enhanced by digital threats. Future energy systems will rely on digital infrastructure to a much larger extent than it exists already today. The multiple couplings between energy sectors in real time and the volatility issues demand for a highly integrated measurement and control system. Technical failures and hacking attacks make such systems highly vulnerable with still few measures possible for effective protection and “hardening” of the systems. It can be expected that the resulting complexity may become a serious obstacle in constructing and operating future energy systems. Conventional electro-mechanical storage systems are not any better in this respect but carry other technical risks (battery fires, breaking dams) than chemical energy storage systems. These safety issues need constant care and open addressing in the essential dialogue with the public, being the users of the energy system. The example of nuclear power with its lost opportunities for safer energy supply sends a clear signal that safety aspects in energy systems are critical both in technical and in communication respects.
This activity is the by far most critical action to initiate a coordinated energy transition. It is more important than liberating limited financial public resources. These can trigger action and should co-finance science and technology, including demonstrations in world-scale. The main body of resources must come from private investments requiring as foundation the stable existence of the roadmap and the two initial concepts.
The roadmap activity needs amongst multiple other issues some planning of the allocation of RE and imports as hydrogen and derivatives to major energy users, to enable designing infrastructures of suitable dimension and topology. Such planning further needs avoiding double allocation of local RE for immediate electrical use and for CEC applications for example by demanding a suitable market design.
Science for energy conversion may follow a dual strategy. One arm covers the world-scale initiation of a generation 1 (G1) CEC component of energy systems whereas the other arm should provide radically innovative approaches dealing with the minimization of the systemic inefficiencies of the G1 system. This will need deep insight into fundamental processes of interfacial and molecular catalysis as the common scientific foundation. Having available a toolbox30 of design and synthesis methodologies, one could design from scratch chains of energy conversion with a maximal systemic efficiency. This may then involve other infrastructures and energy utilization appliances that can be realized after the G1 energy system has provided the climate protection as described in the Paris agreement. In this second arm the scientific creativity of basic science bare of constraints from techno-economic realizability is key to provide an ecosystem of options from which future concepts can begin to deal with the massive challenge of converting science into technology. In this period the life cycle assessments6 and scalability questions become important; they may be based whenever possible upon data acquired in actual projects rather than on theoretical estimates.
It is important to understand that the G1 science and technologies are of utmost urgency to kick off the energy system transformation that will not come only from providing locally RE to the existing energy system. Rather, establishing a circular economy of carbon-based synthetic fuels23,31 besides a suitable technology portfolio for global hydrogen exchange32 are the actions needed now. A key issue is here the suitable integration of life cycle analysis in choosing the technology options33 for example under conditions of “mixed” electrical energy supply containing fossil and RE components. Challenges34 of system integration and operation control of dynamical energy supply structures,35 engineering issues and the scaling of production of devices and systems required for CEC (electrolysers, CEC plants, small scale decentralized units) are the pressing issues. Digitalization of discovery processes30,36 and their scale-up, material science and the molecular understanding of the underlying processes of chemical conversion37 are cross-linking basic components of an integrated research and technology innovation roadmap representing an integral part of the transformation roadmap.
At present science is far away from such a coordinated and prioritized action. The essential plurality of communities involved may largely preclude substantial progress in coordination (as it may hamper creativity). An important step forward, however, could be done if in science the documentation of results and insights would occur in a clean and complete manner such that later the developing tools of artificial intelligence can re-use the information independent of its original context. The author strongly advertises a community-internal effort (see e.g.https://nomad-coe.eu) to develop a standard of minimum quality reporting for energy-related work. This would not inhibit creativity by limitations imposed but multiply the usefulness of the ongoing rich scientific activities.
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