Abstract

The Paris Agreement’s temperature goals require global CO2 emissions to halve by 2030 and reach net zero by 2050. CO2 capture and utilization (CCU) technologies are considered promising to achieve the temperature goals. This paper investigates which CCU technologies—using atmospheric, biogenic, or fossil CO2—are Paris compatible, based on life cycle emissions and technological maturity criteria. We systematically gathered and harmonized CCU technology information for both criteria and found that CCU with technology readiness levels (TRLs) of 6 or higher can be Paris compatible in 2030 for construction materials, enhanced oil recovery, horticulture industry, and some chemicals. For 2050, considering all TRLs, we showed that only products storing CO2 permanently or produced from only zero-emissions energy can be Paris compatible. Our findings imply that research and policy should focus on accelerating development of CCU technologies that may achieve (close to) zero net emissions, avoiding lock-in by CCU technologies with limited net emission reductions. The Paris Agreement’s temperature goals require global CO2 emissions to halve by 2030 and reach net zero by 2050. CO2 capture and utilization (CCU) technologies are considered promising to achieve the temperature goals. This paper investigates which CCU technologies—using atmospheric, biogenic, or fossil CO2—are Paris compatible, based on life cycle emissions and technological maturity criteria. We systematically gathered and harmonized CCU technology information for both criteria and found that CCU with technology readiness levels (TRLs) of 6 or higher can be Paris compatible in 2030 for construction materials, enhanced oil recovery, horticulture industry, and some chemicals. For 2050, considering all TRLs, we showed that only products storing CO2 permanently or produced from only zero-emissions energy can be Paris compatible. Our findings imply that research and policy should focus on accelerating development of CCU technologies that may achieve (close to) zero net emissions, avoiding lock-in by CCU technologies with limited net emission reductions. In the 2015 Paris Agreement, almost all of the world’s nations committed to collectively hold “the increase in the global average temperature to well below 2°C above pre-industrial levels and pursuing efforts to limit the temperature increase to 1.5°C above pre-industrial levels.”2UNFCCCDecision 1/CP.21: adoption of the Paris agreement.in: Report of the Conference of the Parties on its Twenty-First Session, Held in Paris From 30 November to 13 December 2015. Addendum: Part Two: Action Taken by the Conference of the Parties at Its Twenty-First Session FCCC/CP/2015/10/Add.1. United Nations Framework Convention on Climate Change (UNFCCC), 2016: 1-36Google Scholar This is also known as the Paris Agreement’s long-term temperature goal (LTTG). Climate change mitigation pathways with “no or low overshoot” of 1.5°C3Rogelj J. Shindell D. Jiang K. Fifita S. Forster P. Ginzburg V. Handa C. Kheshgi H. Kobayashi S. Kriegler E. et al.Mitigation pathways compatible with 1.5°C in the context of sustainable development.in: Global Warming of 1.5°C. An IPCC Special Report on the Impacts of Global Warming of 1.5°C Above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to the Threat of Climate Change. 2018Google Scholar are compatible with the Paris Agreement’s LTTG4Wachsmuth J. Schaeffer M. Hare B. The EU long-term strategy to reduce GHG emissions in light of the Paris agreement and the IPCC special report on 1.5°C. No. S 22/2018. 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Kheshgi H. Kobayashi S. Kriegler E. et al.Mitigation pathways compatible with 1.5°C in the context of sustainable development.in: Global Warming of 1.5°C. An IPCC Special Report on the Impacts of Global Warming of 1.5°C Above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to the Threat of Climate Change. 2018Google Scholar This net zero CO2 target implies that no sector can be excluded from deep emission reductions, that some technologies that still have significant emissions need to be phased out, and that a range of technologies is required to reach these emission reductions. Carbon (dioxide) capture and utilization (CCU) is among these options for potential emission reduction and is defined here as a process in which CO2 is technologically captured from CO2 point sources or ambient air and is subsequently used in or as a product. The reason why CCU could contribute to climate change mitigation is that it replaces fossil feedstocks, avoids upstream emissions, and temporarily keeps CO2 out of the atmosphere until re-emitted in the use phase of the product.8Núñez-López V. Gil-Egui R. Hosseini S. Environmental and operational performance of CO2-EOR as a CCUS technology: a cranfield example with dynamic LCA considerations.Energies. 2019; 12: 448Crossref Google Scholar, 9Chauvy R. Meunier N. Thomas D. de Weireld G. Selecting emerging CO2 utilization products for short- to mid-term deployment.Appl. Energy. 2019; 236: 662-680Crossref Scopus (18) Google Scholar, 10Kätelhön A. Meys R. Deutz S. Suh S. Bardow A. Climate change mitigation potential of carbon capture and utilization in the chemical industry.Proc. Natl. Acad. Sci. 2019; 116: 11187-11194Crossref PubMed Scopus (0) Google Scholar, 11Hepburn C. Adlen E. Beddington J. Carter E.A. Fuss S. Mac Dowell N. Minx J.C. Smith P. Williams C.K. The technological and economic prospects for CO2 utilization and removal.Nature. 2019; 575: 87-97Crossref PubMed Scopus (326) Google Scholar, 12Thonemann N. Pizzol M. Consequential life cycle assessment of carbon capture and utilization technologies within the chemical industry.Energy Environ. Sci. 2019; 12: 2253-2263Crossref Google Scholar, 13Detz R.J. van der Zwaan B. Transitioning towards negative CO2 emissions.Energy Policy. 2019; 133: 110938Crossref Scopus (18) Google Scholar CCU is distinguished from (permanent) carbon dioxide removal (CDR) of atmospheric CO2. The two terms only overlap when CO2 in a CCU product has recently been removed from the atmosphere and is never re-emitted.14IPCCAnnex I: glossary.in: Global Warming of 1.5°C. An IPCC Special Report on the Impacts of Global Warming of 1.5°C Above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to the Threat of Climate Change. 2018Google Scholar CCU appeals to policymakers and the general public because it is seen as part of the circular economy and a form of sustainable waste processing.15Styring P. Jansen D. de Coninck H. Reith H. Armstrong K. Carbon Capture and Utilisation in the Green Economy. The Centre for Low Carbon Futures 2011 and CO2Chem Publishing, 2011Google Scholar It also appeals to industry because CCU creates value from waste through CO2-based products16Cuéllar-Franca R.M. Azapagic A. Carbon capture, storage and utilisation technologies: a critical analysis and comparison of their life cycle environmental impacts.J. CO2 Util. 2015; 9: 82-102Crossref Scopus (720) Google Scholar,17IEATransforming Industry Through CCUS. International Energy Agency, 2019Google Scholar while avoiding the storage costs and concerns of geological storage of captured CO2, known as carbon (dioxide) capture and storage (CCS).18Lilliestam J. Bielicki J.M. Patt A.G. Comparing carbon capture and storage (CCS) with concentrating solar power (CSP): potentials, costs, risks, and barriers.Energy Policy. 2012; 47: 447-455Crossref Scopus (70) Google Scholar However, the relevance of CCU in climate change mitigation is questioned in the literature, based on several concerns: (1) CCU products may not always substantially reduce emissions compared with their conventional counterparts that do not require the energy-intensive CO2 capture and conversion steps;19Abanades J.C. Rubin E.S.S. Mazzotti M. Herzog H.J.J. On the climate change mitigation potential of CO2 conversion to fuels.Energy Environ. Sci. 2017; 10: 2491-2499Crossref Google Scholar, 20Garcia-Herrero I. Cuéllar-Franca R.M. Enríquez-Gutiérrez V.M. Alvarez-Guerra M. Irabien A. Azapagic A. Environmental assessment of dimethyl carbonate production: comparison of a novel electrosynthesis route utilizing CO2 with a commercial oxidative carbonylation process.ACS Sustain. Chem. Eng. 2016; 4: 2088-2097Crossref Scopus (55) Google Scholar, 21Mac Dowell N. Fennell P.S. Shah N. Maitland G.C. The role of CO2 capture and utilization in mitigating climate change.Nat. Clim. Chang. 2017; 7: 243-249Crossref Scopus (394) Google Scholar, 22Bruhn T. Naims H. Olfe-Kräutlein B. Separating the debate on CO2 utilisation from carbon capture and storage.Environ. Sci. Policy. 2016; 60: 38-43Crossref Google Scholar (2) utilization of captured CO2, rather than permanent geological storage, may result in a higher global warming effects because utilized CO2 is typically re-emitted when the CCU product is used or disposed of;16Cuéllar-Franca R.M. Azapagic A. Carbon capture, storage and utilisation technologies: a critical analysis and comparison of their life cycle environmental impacts.J. CO2 Util. 2015; 9: 82-102Crossref Scopus (720) Google Scholar,19Abanades J.C. Rubin E.S.S. Mazzotti M. Herzog H.J.J. On the climate change mitigation potential of CO2 conversion to fuels.Energy Environ. Sci. 2017; 10: 2491-2499Crossref Google Scholar (3) CCU may not be economically feasible because of the high financial costs associated with the energy-intensive CO2 capture and conversion steps;19Abanades J.C. Rubin E.S.S. Mazzotti M. Herzog H.J.J. On the climate change mitigation potential of CO2 conversion to fuels.Energy Environ. Sci. 2017; 10: 2491-2499Crossref Google Scholar,23Fernández-Dacosta C. Shen L. Schakel W. Ramirez A. Kramer G.J. Potential and challenges of low-carbon energy options: comparative assessment of alternative fuels for the transport sector.Appl. Energy. 2019; 236: 590-606Crossref Scopus (54) Google Scholar and (4) CCU may form a political distraction from reducing CO2 emissions, in particular when replacing CCS, because the scale at which CO2 could be utilized is limited compared with the scale at which CO2 could be stored geologically.21Mac Dowell N. Fennell P.S. Shah N. Maitland G.C. The role of CO2 capture and utilization in mitigating climate change.Nat. Clim. Chang. 2017; 7: 243-249Crossref Scopus (394) Google Scholar The goal of this review is to provide conceptual clarity on what CCU is and what can be expected from different CCU technological routes, in particular in reaching the Paris Agreement’s LTTG. We first describe the different process steps and varieties of CCU technologies. Next, we present a framework to assess “Paris compatibility” in the context of CCU, using criteria based on technological maturity and greenhouse gas emissions reductions. We then show the results of a systematic review of the CCU literature following this framework. Last, we discuss our findings and provide a research and policy outlook for climate change mitigation through CCU. For an overview of acronyms used, see Note S1. In line with our definition of CCU, we defined six key characteristics of CCU (Figure 1):(A)Sources of CO2. CO2 can originate from fossil fuel or biomass combustion in power plants or industrial plants, from industrial processes such as the calcination reaction in cement production or biomass fermentation, or from the atmosphere directly using direct air capture (DAC).(B)Capture of CO2. CO2 is captured technologically on an industrial scale by separating CO2 from a bulk gas stream or the atmosphere using a solvent or sorbent, a membrane, cryogenics, or industrially cultivated organisms, such as microalgae, to photosynthesize CO2 into biomass.(C)Utilization of CO2. CO2 is used directly or indirectly by converting CO2 into a range of products, often requiring electricity, heat, and/or catalysts.(D)CCU categories. The resulting CCU products can be categorized as direct uses, enhanced hydrocarbon recovery (EHR), mineral carbonates and construction materials, and fuels and chemicals.(E)Substitute. A CCU product is assumed to replace a product in the conventional economy with the same chemical structure, composition, or characteristics, typically produced from fossil fuels and referred to as the substitute.24Zimmermann A.W. Wunderlich J. Müller L. Buchner G.A. Marxen A. Michailos S. Armstrong K. Naims H. McCord S. Styring P. et al.Techno-economic assessment guidelines for CO2 utilization.Front. Energy Res. 2020; 8: 5Crossref Scopus (0) Google Scholar(F)CCU lifetime. CO2 is, depending on the CCU product, stored permanently or released into the atmosphere after a certain period of time, called its lifetime, ranging from days to centuries. For example, for fuels, the utilized CO2 is emitted into the air upon combustion. For the purpose of this paper, we define storage as reaching permanency when it has a duration consistent with geological timescales: centuries or longer. Because we consider CCU for climate change mitigation, we exclude the use of CO2 from natural reservoirs because this source of CO2 does not reduce atmospheric CO2 concentrations.25NETLCarbon Dioxide Enhanced Oil Recovery - Untapped Domestic Energy Supply and Long Term Carbon Storage Solution. National Energy Technology Laboratory. U.S. Department of Energy, 2010Google Scholar Our definition of CCU constrains CCU to processes that “technologically capture CO2,” including industrial and engineered biological processes such as CO2 capture from flue gases by microalgae, and excluding land-based CO2 sequestration in biomass (in contrast to, for example, Detz and van der Zwaan13Detz R.J. van der Zwaan B. Transitioning towards negative CO2 emissions.Energy Policy. 2019; 133: 110938Crossref Scopus (18) Google Scholar and Hepburn et al.11Hepburn C. Adlen E. Beddington J. Carter E.A. Fuss S. Mac Dowell N. Minx J.C. Smith P. Williams C.K. The technological and economic prospects for CO2 utilization and removal.Nature. 2019; 575: 87-97Crossref PubMed Scopus (326) Google Scholar). Use of biomass for energy and materials is therefore also not in the scope of this review. CCU is sometimes connected to CDR. CDR is a necessity to limit warming to 1.5°C3Rogelj J. Shindell D. Jiang K. Fifita S. Forster P. Ginzburg V. Handa C. Kheshgi H. Kobayashi S. Kriegler E. et al.Mitigation pathways compatible with 1.5°C in the context of sustainable development.in: Global Warming of 1.5°C. An IPCC Special Report on the Impacts of Global Warming of 1.5°C Above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to the Threat of Climate Change. 2018Google Scholar and has been defined as “anthropogenic activities removing CO2 from the atmosphere and durably storing it in geological, terrestrial, or ocean reservoirs, or in products.”14IPCCAnnex I: glossary.in: Global Warming of 1.5°C. An IPCC Special Report on the Impacts of Global Warming of 1.5°C Above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to the Threat of Climate Change. 2018Google Scholar CDR includes methods like bioenergy with CCS (BECCS) and direct air CCS (DACCS).26de Coninck H. Revi A. Babiker M. Bertoldi P. Buckeridge M. Cartwright A. Dong W. Ford J. Fuss S. cade J.-C. et al.Strengthening and implementing the global response.in: Masson-Delmotte V. Zhai P. Pörtner H.-O. Roberts D. Skea J. Shukla P.R. Pirani A. Moufouma-Okia W. Péan C. Pidcock R. Global Warming of 1.5°C. An IPCC Special Report on the Impacts of Global Warming of 1.5°C Above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to the Threat of Climate Change. 2018Google Scholar CCU can only be classified as CDR, following the criteria formulated by Tanzer and Ramírez,27Tanzer S.E. Ramírez A. When are negative emissions negative emissions?.Energy Environ. Sci. 2019; 12: 1210-1218Crossref Google Scholar when (1) physical CO2 is removed from atmosphere by capturing CO2 directly from the air or capturing CO2 from a biogenic source, (2) the CO2 is stored permanently and not re-emitted to the atmosphere at a later point, and (3) the net quantity of CO2 stored permanently through CCU is greater than the quantity of CO2 emitted over the product’s full life cycle, including use of the product and the emissions associated with the energy required for the CO2 capture and conversion processes. When the criteria for CDR are not met but the life cycle emissions are lower than for the substituted product, CCU is considered a climate change mitigation measure. Avoided emissions compared with the substituted product may be presented as a negative number but should not be confused with physical removal of CO2 from the atmosphere.27Tanzer S.E. Ramírez A. When are negative emissions negative emissions?.Energy Environ. Sci. 2019; 12: 1210-1218Crossref Google Scholar CO2 is typically captured from a point source, such as flue gas streams at power plants or industrial plants, or from industrial processes where CO2 is produced as a by-product. Capturing CO2 from a bulk gas stream entails separating the CO2 from the rest of the stream. Sometimes CO2 separation is already required in the primary production process; for example, in ammonia synthesis, natural gas processing, and biogas upgrading to biomethane.28IPCCSpecial report on carbon dioxide capture and storage.in: Metz B. Davidson O. de Coninck H.C. Loos M. Meyer L.A. Prepared by Working Group III of the Intergovernmental Panel on Climate Change. Cambridge University Press, 2005Google Scholar This leads to a high-purity stream of CO2 along with the primary product. Depending on the concentration and components present in a gas stream, one of three main separation processes may be most suitable29Ramírez-Santos Á.A. Castel C. Favre E. A review of gas separation technologies within emission reduction programs in the iron and steel sector: current application and development perspectives.Sep. Purif. Technol. 2018; 194: 425-442Crossref Scopus (0) Google Scholar: (1) absorption of CO2 in a liquid solvent, (2) adsorption of CO2 onto a solid, and (3) using a membrane to separate CO2 through selective permeability.30Leonzio G. State of art and perspectives about the production of methanol, dimethyl ether and syngas by carbon dioxide hydrogenation.J. CO2 Util. 2018; 27: 326-354Crossref Scopus (71) Google Scholar In CO2 absorption processes using amine-based solvents like monoethanolamine, CO2 is chemically bound, and then the CO2 is stripped to allow the solvent to absorb CO2 again in the next cycle. This is called regeneration of the solvent and requires heat. Besides single-amine absorption, amine blends are in development where amines are combined for complementary characteristics. An integrated CCU process has also been proposed to reduce the overall energy demand, absorbing CO2 from raw natural gas in methanol, after which conversion takes place.31Jens C.M. Müller L. Leonhard K. Bardow A. To integrate or not to integrate—techno-economic and life cycle assessment of CO2 capture and conversion to methyl formate using methanol.ACS Sustain. Chem. Eng. 2019; 7: 12270-12280Google Scholar Other developments include ionic liquids, which are liquids composed entirely of ions with a melting point of less than 100°C.32Bui M. Adjiman C.S. Bardow A. Anthony E.J. Boston A. Brown S. Fennell P.S. Fuss S. Galindo A. Hackett L.A. et al.Carbon capture and storage (CCS): the way forward.Energy Environ. Sci. 2018; 11: 1062-1176Crossref Google Scholar Physical adsorption research has focused on improving the adsorbents as well as the adsorption processes of regeneration.32Bui M. Adjiman C.S. Bardow A. Anthony E.J. Boston A. Brown S. Fennell P.S. Fuss S. Galindo A. Hackett L.A. et al.Carbon capture and storage (CCS): the way forward.Energy Environ. Sci. 2018; 11: 1062-1176Crossref Google Scholar Alternatives, like high-temperature solid adsorption of CO2, require less energy input for regeneration compared with low-temperature liquid absorption.33Ben-Mansour R. Habib M.A. Bamidele O.E. Basha M. Qasem N.A.A. Peedikakkal A. Laoui T. Ali M. Carbon capture by physical adsorption: materials, experimental investigations and numerical modeling and simulations – a review.Appl. Energy. 2016; 161: 225-255Crossref Scopus (300) Google Scholar, 34Ho M.T. Bustamante A. Wiley D.E. Comparison of CO2 capture economics for iron and steel mills.Int. J. Greenh. Gas Control. 2013; 19: 145-159Crossref Scopus (53) Google Scholar, 35Manzolini G. Giuffrida A. Cobden P.D. van Dijk H.A.J. Ruggeri F. Consonni F. Techno-economic assessment of SEWGS technology when applied to integrated steel-plant for CO2 emission mitigation.Int. J. Greenh. 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Because atmospheric CO2 concentrations (approximately 400 ppm) are 100–300 times lower than for point sources, energy requirements, and therefore costs, for DAC are substantially larger than for point source capture.41Fasihi M. Efimova O. Breyer C. Techno-economic assessment of CO2 direct air capture plants.J. Clean. Prod. 2019; 224: 957-980Crossref Scopus (203) Google Scholar,42de Jonge M.M.J. Daemen J. Loriaux J.M. Steinmann Z.J.N. Huijbregts M.A.J. Life cycle carbon efficiency of Direct Air Capture systems with strong hydroxide sorbents.Int. J. Greenh. Gas Control. 2019; 80: 25-31Crossref Scopus (27) Google Scholar Expert elicitation leads to expected cost declines to around 200 US dollars (USD) per ton of CO2 captured by 2050,43Shayegh S. Bosetti V. Tavoni M. Future prospects of direct air capture technologies: insights from an expert elicitation survey.Front. 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