Anahita
Mani
,
Thomas
Budd
and
Elicia
Maine
Simon Fraser University (SFU), British Columbia, Canada
First published on 22nd December 2023
It is critically important to pursue the decarbonization of emissions-intensive and trade-exposed (EITE) industries in British Columbia (BC) and Canada and successfully integrate innovation-supporting policies with decarbonization policies designed to rapidly reduce industrial greenhouse gas (GHG) emissions. Focusing on EITE industries in BC, we have investigated the potential of decarbonization in five sectors: oil and gas, pulp and paper, aluminum smelting, cement clinker manufacturing, and mining. This paper examines available net-zero carbon technologies that these EITE industries could potentially adopt to achieve decarbonization targets. The key technologies identified are hydrogen, carbon capture and digitalization. Additionally, we identify continued innovation policy and support to promote the growth and prosperity of a low-carbon supply chain, BC's industrial competitiveness, and the scale-up of renewable companies and infrastructure. To aid public and private sectors in striving for sustainable pathways to decarbonization, we have developed a Technology Roadmap for BC to help policymakers and firms formulate a climate change mitigation strategy employing innovative technologies for large industrial emitters. Our analysis indicates renewable and low carbon intensity fuels such as hydrogen can play a vital role in reducing emissions across a wide range of BC's EITE sectors (i.e., displacing diesel and eventually natural gas), thus having economic and environmental benefits for BC.
Sustainability spotlightAchieving global greenhouse gas (GHG) emissions reductions to net-zero by 2050 requires the decarbonization of emissions-intensive and trade-exposed (EITE) industrial sectors. Using British Columbia, Canada as a case study, a Technology Roadmap was developed for five difficult to abate industrial sectors: oil and gas, pulp and paper, aluminum smelting, cement clinker manufacturing, and mining. The roadmap is designed to provide policymakers and firms a means to develop GHG reduction and technology innovation strategies to both mitigate EITE emissions and to develop BC’s clean energy sector. This work focuses on the UN sustainable development goals of affordable and clean energy (SDG 7), industry, innovation, and infrastructure (SDG 9), climate action (SDG 13). |
Special consideration must be given to EITEs because, if faced with sudden, substantial changes and cost increases in their operations, demand for their products could transfer elsewhere in the global market without reducing worldwide emissions.2,7,10 GHG reduction is a global collective action problem in that virtually all countries must participate to produce the desired outcome. Thus, efforts by one country to unilaterally reduce emissions in its EITE industries will cause competitive problems regarding the industries located in countries that lack stringent GHG-reducing policies. This competitive loss is sometimes referred to as “carbon leakage” to denote that any shifts in production could likely leak the emissions to elsewhere on the planet rather than reducing them.2
Canada's GHG emissions (Fig. 1), as reported in 2019, were 730 Mt, unchanged since 2005. With 19.7 tonnes of CO2 per capita emitted, this makes Canada's emissions the third-highest per capita amongst the thirty-six Organisation for Economic Co-operation and Development (OECD) members.11 Nevertheless, Canada has implemented climate policies, including a nationwide carbon price, which is reflected in the cost of fossil fuels used in all sectors of the economy.12Fig. 1 illustrates Canada's GHG emissions, broken out by economic sector, which is displayed on a map of Canada in Fig. 2.
Fig. 1 Canada's GHG emissions, broken out by economic sector. Image: adapted from National Inventory Report 2021.14 |
Fig. 2 2021 facility greenhouse gas (GHG) emissions. Image: courtesy of Environment and Climate Change Canada (ECCC).19 |
EITE industries are hard to decarbonize because they produce and export commodity materials which are sensitive to price changes. The processes contributing to GHG for each EITE industrial sector in BC are described in Table 1. Decarbonization efforts are made further complex by industrial processes and infrastructure that are primarily compatible with conventional energy GHG emitting sources rather than those provided by innovative low carbon technologies. To transition industries away from high carbon-intensive energy, renewable and other low emitting energy sources will need to be compatible with existing industrial processes, allowing for their adoption at low cost. To survive, EITE industries will need to maintain continuous operation by having access to reliable sources of energy and consumer markets at a time where there will be rapid and significant transitions in both energy generation and consumer purchasing behavior.6,15
EITE industries | |
---|---|
Aluminium sector | Primary aluminum production through smelting and refining and secondary aluminum production in which aluminum is recovered from aluminum-containing scrap.23,24 |
Mining sector | Overburden removal, drilling in rock, blasting, crushing of rock, loading of materials, transporting raw materials by conveyors, scraping, bulldozing, grading, open storage pile losses and wind erosion from exposed areas.25,26 |
Cement sector | The entire process of cement production in rotary kilns, as well as the preparation of concrete and ready-mix concrete, lime manufacture and concrete batching and products27 |
Pulp and paper sector | Chemical, mechanical, recycling, and semi-chemical mills, including the production of energy through the combustion of spent pulping liquor, biomass, and fossil-fuel combustion. Also includes fugitive emissions from wood refining, screening, and drying, and various steps in chemical recovery systems28 |
Sawmills, panel board mills (including veneer, plywood, waferboard, particleboard and medium-density fiberboard mills), and other wood products manufacturing establishments (including furniture and cabinet makers, wood treating plants, wood pellet mills and Masonite manufacturers)29 | |
Oil and gas/Refine petroleum products sector | Electric power generation from the combustion of fossil fuels by utilities (both publicly and privately owned) for commercial sale and/or private use30 |
Solutions that capture CO2 from facility emissions or directly from the atmosphere are also required for EITE decarbonization.14 Technology options that include negative emissions such as direct air capture (DAC) and other carbon capture techniques will enable governments to implement more stringent decarbonization policies while potentially maintaining established homegrown carbon-intensive industries.7,8,16 Carbon capture systems that both used and store CO2 are often called carbon capture, utilization, and storage (CCU/S); here we use the term ‘CCU/S’. However, while removing CO2 is necessary, at least in the near-term future, the use of renewable and net-zero carbon sources of energy must be integrated if 2050 net-zero emission reduction goals are to be met. Industries have access to CCU/S and other technologies that would achieve a 100% fossil fuel global energy system with virtually zero GHG emissions, but the cost is currently too high for 100% adoption in EITE sectors.17
BC's total GHG emission inventories, measured in tonne of CO2 equivalent (tCO2e), is collected by government for the five main EITE industrial sectors. Aluminum, Cement, Pulp and Paper, Mining, and Oil & Gas, based on their NAICS Code, company name and facility name are shown in Table 2 and Fig. 3a. The transportation sector is not considered an EITE industry, however, oil and gas production and transportation emissions data are included. The bar plot in Fig. 3b demonstrates that BC's oil and gas sector has the largest carbon footprint compared with BC's remaining EITE sectors. The bar plot in Fig. 3c displays total BC oil and gas sector GHG emissions (tCO2e) by production, transportation and refining.
Primary activity NAICS code & description | Company name | Facility name | Grand total emissions tCO2e |
---|---|---|---|
211113-Conventional Oil and Gas Extraction | ARC Resources | ARC BC LFO | 359529 |
211113-Conventional Oil and Gas Extraction | Canadian Natural Resources Ltd | CNRL BC LFO | 1124122 |
211113-Conventional Oil and Gas Extraction | EnCana Corporation | Encana BC LFO | 987348 |
211113-Conventional Oil and Gas Extraction | NorthRiver Midstream Inc. | BC Midstream (LFO) | 417803 |
211113-Conventional Oil and Gas Extraction | PETRONAS Energy Canada Ltd | Petronas Linear Facilities Operation | 543546 |
211113-Conventional Oil and Gas Extraction | Spectra Energy Transmission | SET PLFS (LFO) | 2692139 |
211113-Conventional Oil and Gas Extraction | Tourmaline Oil Corp | Tourmaline LFO | 427722 |
211113-Conventional Oil and Gas Extraction | Canadian Natural Resources Ltd | BC Aggregated Facilities (<10000 tCO2e) | 558348 |
211113-Conventional Oil and Gas Extraction | Spectra Energy Transmission | Fort Nelson Gas Plant | 503025 |
212114-Bituminous Coal Mining | Teck Coal Limited | Elkview Operations | 458448 |
212114-Bituminous Coal Mining | Teck Coal Limited | Fording River Operations | 573128 |
212114-Bituminous Coal Mining | Teck Coal Limited | Greenhills Operations | 408459 |
322111-Mechanical Pulp Mills | Catalyst Paper Corporation | Powell River Division | 671467 |
322112-Chemical Pulp Mills | Canfor Pulp Ltd | Prince George Pulp & Paper Mill | 2118021 |
322112-Chemical Pulp Mills | Cariboo Pulp and Paper Co | Cariboo Pulp and Paper Company | 1318150 |
322112-Chemical Pulp Mills | Catalyst Paper Corporation | Crofton Division | 1674233 |
322122-Newsprint Mills | Catalyst Paper Corporation | Port Alberni Division | 427714 |
322112-Chemical Pulp Mills | Canfor Pulp Ltd | Northwood Pulp Mill | 1487002 |
322112-Chemical Pulp Mills | Domtar Inc. | Kamloops Mill (SFO) | 1327266 |
322112-Chemical Pulp Mills | Howe Sound Pulp & Paper Corp | Howe Sound Pulp and Paper Mill | 1446618 |
322112-Chemical Pulp Mills | Mackenzie Pulp Mill Corp. | Mackenzie Pulp Mill | 697670 |
322112-Chemical Pulp Mills | Mercer Celgar Ltd Partnership | Mercer Celgar Limited Partnership | 1330736 |
322112-Chemical Pulp Mills | Nanaimo Forest Products Ltd | Harmac Pacific Operations | 1283000 |
322112-Chemical Pulp Mills | Skookumchuck Pulp Inc. | Skookumchuck Operation | 986342 |
324110-Petroleum Refineries | Parkland Refining (B.C.) Ltd | Burnaby Refinery | 427960 |
327310-Cement Manufacturing | Lafarge Canada Inc. | Richmond Cement Plant | 658346 |
327310-Cement Manufacturing | Lehigh Hanson Materials Ltd | Delta Plant | 873630 |
331313-Aluminum Production | Rio Tinto Alcan Inc. | Rio Tinto Alcan Inc. | 836570 |
486210-Pipeline Transportation of Natural Gas | TransCanada PipeLines Ltd | TransCanada Pipeline, BC System | 396605 |
486210-Pipeline Transportation of Natural Gas | Spectra Energy Transmission | Transmission Mainline | 1080113 |
Summation | 28095058 |
Fig. 3 (a) The bar plot displays total GHG emissions (tCO2e) for each BC company and facility classified as EITE; (b) total GHG emissions (tCO2e) collection by sector, Aluminum, Cement, Pulp & Paper, Mining, and Oil & Gas; (c) the bar plot displays total GHG emissions (tCO2e) breakdown in BC's Oil & Gas sector. Notes: oil & gas and mining are not directly shown. Source: Authors' analysis based on data from the Government of British Columbia.39 |
Low carbon intensity technologies are rapidly improving, making it easier for EITE industries to reduce emissions and thus enable governments to implement more stringent emissions policies. Innovative technologies continue to emerge to potentially accelerate decarbonization. Solar Photovoltaics (PV), wind turbines, clean hydrogen, and CCU/S are emerging low carbon intensity technologies relevant to EITEs.
Costs of PV modules and wind turbines have been reduced by nearly 90% and 60%, respectively.20 The cost of constructing and operating wind and solar power plants, as being non-dispatchable electricity, can be compatible with resources that produce dispatchable electricity, with dispatchable electricity being up to 10 times more valuable.21 Utility-scale battery storage technology is also improving and becoming less costly, as the energy cost for lithium-ion battery storage dropped 76% by 2019,32 resulting in easier decarbonizing of electricity systems, particularly in the mining and aluminum sectors. Development of battery and storage technologies will complement non-dispatchable renewable energy investments by storing excess variable renewable generation, thus permitting renewable electricity sources to replace more reliable and consistent fossil fuel based generation without major new investments in conventional and dispatchable large hydro electricity.33
Hydrogen could be considered a promising clean, zero-carbon fuel1,10 to replace carbon-intensity fuels such as oil & gas and coal. The challenge is that while hydrogen exists in nature, it is not capturable in that state. As such, hydrogen is not a primary energy source. Instead, it is an energy vector (a form of secondary energy), like electricity, heat, processed natural gas and refined petroleum products. Recently, the rate of development of facilities for hydrogen production has increased in North America compared with the past decade.15 The potential for hydrogen to transform Canada's economy to a low-carbon future was discussed at the 13th Canadian Science Policy Conference (CSPC)34 as well as at the Canadian Climate Institute (CCI), where experts from diverse disciplines gathered together to undertake rigorous research and conduct insightful analyses.6 However, there is still a need for a range of innovative technologies to utilize hydrogen as a source of industrial decarbonization and the need for transformative policy support by BC's provincial government. Clean hydrogen can be made through several production methods, including biomass and water electrolysis. A recent update on progress in the Canada's emerging hydrogen marketplace,35–37 showed that a lack of sufficient levels of research and development (R&D) funding and large-scale investments may cause a slowdown in an expansion of hydrogen production and use that could achieve emissions reduction targets.38
Recent studies and strategies have compared clean and renewable technologies, typically assuming high carbon capture rates,16 but have not assessed the impact of fugitive emissions and carbon leakage, nor the capture rates on both total emissions and costs.
In this paper, we develop and discuss a Technology Roadmap for EITE industries in BC, where homegrown innovation drives new advances and keeps BC's industries competitive while meeting climate targets within these industrial sectors. Technology strategy from roadmap to action for the next three decades is demonstrated below for BC's five main EITE industrial sectors: aluminum, pulp and paper, oil and gas, cement, and mining.42 Furthermore, we report a pathway for a homegrown, innovative technology analysis to assess the state of relevant technologies and identify critical R&D opportunities to improve further cost competitiveness and lower GHG emissions.
Our study's primary goal is to evaluate different clean technologies and innovative technology options to ensure energy security for BC's EITE industries, thereby establishing the technology roadmap as a critical tool to achieve BC's decarbonization goal by 2050. Our research question is, “How can innovation policy complement decarbonization policies to achieve economic and climate goals in the EITE sectors in BC.” We address this research question through a case study analysis of BC EITE industries and a technology roadmap of the innovative technologies which can achieve decarbonization.
Our methodology used to develop a decarbonization Technology Roadmap for BC's EITE sectors consisting of four phases of research and analysis:
(1) Evidence gathering and processing based on literature.
(2) Analysis of net-zero pathways incorporating BC's preferences and constraints within each EITE sector. Benchmarking overall levels of CO2 emissions reductions that correspond with net-zero goals.
(3) Testing and developing a final pathway that requires vast amounts of investment, innovation and technology deployment, infrastructure modifications, policy implementation, and cooperation across the EITE industries within BC and nationwide. Validating and refining the roadmap through interviews and Pacific Institute for Climate Solutions (PICS) hosted workshops.
(4) Implementing short-term and long-term decarbonization policies and actions necessary to achieve a net-zero by 2050 emissions target.
The timeline of our roadmap was set out to achieve a commitment of having five low-carbon EITE sectors by 2030 and the first net-zero EITE sector by 2040. Our technology roadmap development was based on a comparison of the key points arising from each emissions-reducing innovative technology within its specific value chain segments. Due to the various processing routes of EITE industrial produced materials to the end consumer,53 and their comparatively low emissions, we have not included in our analysis the downstream processing segment of EITE industries, i.e. aluminum, cement and mining into different end-use products. We used an illustrative combined set of four action pathway categories, knowledge and capacity, production or supply, market development demand, and infrastructure material/energy modification (Fig. 9) to facilitate EITE industrial decarbonization. The four categories of actions can be combined for each EITE sectors to show how the most practical or timely elements from each of the innovative technologies can be coordinated to achieve industrial decarbonization. This roadmap could provide government decision makers with insights into potential decarbonization pathways for BC's EITE sectors. The phases used in our analysis to create a novel roadmap are as follows.
We curated those documents for clean energy solutions in the EITE sectors that are most relevant to our policy integration work. Given our expertise in hydrogen production and CCU/S, we were able to take publicly available information on these areas and collate it to inform BC EITE sectors' decarbonization policy. Our team collaborated with Simon Fraser University's Energy and Materials research group to assess and incorporate technical-economic cost data which has been developed by energy modelling experts,7,57 including the federal government's Canadian Centre for Energy Information, Canada Energy Regulator, the U.S. Department of Energy (DOE) Energy Information Administration and the U.S. DOE National Renewable Energy Laboratory.58
Initial technology roadmap inputs were developed by conducting a global literature review on existing research, roadmaps, technical-economic cost modelling methodologies and results.33,54 Our roadmap contributes to the literature and policy discourse by integrating global analyses, applying them to BC's EITE sectors and demonstrating there are pathways to reach net-zero by 2050. Our study considers the potential to achieve emissions reduction targets, technical feasibility, cost-effectiveness, and economic impact in decarbonizing BC EITEs sectors.
Our in-depth literature review looking into currently developed roadmaps and hydrogen strategies reports for Canada and BC provided us with a clear picture of BC's EITE industry infrastructure capabilities and how they align with their decarbonization goals. We adapted this information to be compatible with BC and Canadian context. Secondary data was collecting to assist with forming a complete profile of BC EITE industries.53 Secondary sources include Genesis Advanced Technology, governments of BC and Canada, Sustainable Development Technology Canada (SDTC), and through Cleantech companies' documents, published interviews of industrial leaders, and publicly available information on the company websites. Following Maine et al., these data are supplemented by in-depth searches for research papers, magazine articles and case studies on emerging innovative technologies, their competitors, and technology suppliers.57 A case study approach, is particularly well-suited to develop an understanding of emerging innovative technologies for industries, specifically for addressing “how” and “why” questions.60,61
We investigated the emergence of the green and clean hydrogen sector, which has promising attributes in BC, to develop guidelines for clean hydrogen technology start-ups in emerging innovative technology for the EITE industries. Collecting publicly available secondary data from various sources (including government, regulatory agencies, and company websites), along with online meetings in hydrogen strategy from the founders/CEOs/VPs, allowed us to engage in data analysis to mitigate concerns about the reliability of the study.64 These meetings were conducted during interviews with five industry professionals with engineering design and business development experience. One of the meetings was with a representative from the CCU/S design industry in BC, and another was with an active party in membrane development for green hydrogen production via electrolysis.
Our roadmap provides the relevant timelines and milestones of low-emission innovative technologies that meet BC EITE industries' production requirements. However, to avoid significant technology failures as much as possible, we considered any weaknesses within the industries' existing infrastructure that are currently known. Our roadmap was adapted to the global innovations trends outlined by the IEA36,54 and local consideration through the input of secondary source analyses on clean energy in BC from 25 active companies,53,66,67 of which 12 are the leading companies listed in Global Cleantech 100 (ref. 9) in CCU/S and hydrogen technologies. To achieve decarbonized EITE industries in BC, a joint effort by investors, industries, and policymakers to foster an acceleration of innovative activities along the value chain are required, including industry alliances and companies heavily investing in R&D to developing new low carbon-emitting products. Both industry and regulators must coordinate to push for the enforcement of long-term objectives for decarbonization in general and hydrogen in particular.
We validated our roadmapping methodology by soliciting feedback on our initial analysis through interviews with relevant policy experts and Cleantech industry professionals, including Aaron Hoskin of NRCan,15 and David Sanguinetti of Foresight CAC, and PICS.49 We maintained ongoing collaborations with PICS, Foresight CAC, and BC-based universities throughout our analysis and continually engaged with a network of decision-makers in government and industry as part of designing, implementing, and presenting the results of our research.68
Studying various BC-based innovative technologies71 in varying stages of technology readiness levels (TRL) and best available technology (BAT) within the value chain for each specific tech mechanism greatly contributed to our analysis. The results of this study incorporated R&D and production capacity, market development potential, and supporting infrastructure modification for the five chosen BC EITE industry sectors. We conducted an examination of available cost-effective zero-carbon technologies and industrial processes to develop our decarbonization roadmaps and a ventures database.53 Various pathways among BC's industries were developed to consider the impact of potentially successful and sustainable joint efforts between EITE industrial sectors to decarbonize.42
Our research intends to advance prevailing Energy-Economy-Emissions Models and develop their capacity to assess decarbonization and innovation technology mixes for EITE industries and analyze different combinations of innovation and climate policies under diverse circumstances to reach a net-zero emissions target by 2050.1 While it was beyond the scope of this study to conduct sensitivity analyses on the many different parameters such as the emissions intensity and trade intensity of the five industries studied, important uncertainties were identified and explored in our technology roadmap methodology.
Fig. 4 Lafarge Canada Inc. (Richmond) and Cement – Lehigh Hanson Materials Ltd are the two sectors located across the Fraser River in BC. Image: courtesy of Google Map. |
A summary of all the components necessary to decarbonize cement production processes:
(1) Carbon curing will provide partial reductions by increasing both CO2 efficiency and output efficiency.
(2) “Clinker Substitution” partially reduces clinker use per output of cement or replace with ‘alternative clinker’.
(3) Decarbonizing clinker production could be done by:
(3a) CCU/S for process emissions (when lime is heated), and
(3b) decarbonizing kiln heat source with CCU/S or fuel switching to electricity, biofuel, or hydrogen.44
The Heidelberg Cement Group (Fig. 4) has taken the initiative to decarbonize their processes in three approaches: (1) development of alternative clinker; (2) CCU/S technologies; and (3) developing a composite cement containing less clinker.
In the “Acceleration and Scale-up” stage of technology development, capturing unavoidable process emissions, reusing the CO2 in cement industries, and boosting bio-based concrete73 can be achieved starting with 10000 tonnes per year of production in 2030.
Zero-carbon cement includes all direct CO2 emissions associated with its production and lifetime servicing, as well as all sequestration options, such as engineered re-carbonation, the use of supplementary cementitious materials (SCM) or carbon-free energy sources, electrification, and CCU/S technologies, followed by growth and diversification of the sector in the 2025–2030 timeframe. These technologies are considered in our four action lines (Fig. 8), and in our roadmapping (Fig. 9). As the technology matures or reaches appropriate TRL stages for commercialization, carbon storage use can be focused on applications that provide the best value proposition relative to other zero-emission technologies.
Mechanical pulp mills in BC have always been driven by electricity, ∼100% machine-controlled to separate wood fibres to make pulp.74 While, in chemical pulping, wood fibres are separated through chemical reactions generated with heat, where most decarbonization has occurred by taking the biomass waste from the chemical reactions (known as Black Liquor) to use as an energy source to drive the heating process. Hence, it is a promising approach to decarbonizing heat in the pulp and paper industry, suggesting that black liquor is an option to explore. All black liquor from thermo-chemical pulping, fuels synthesized from biomass via thermochemical conversion processes,66 have been recovered and burned to generate heat since at least the 1960s.75 This on-site recycling process is likely the most accessible and cost-effective way for which pulping mills are rapidly decarbonizing. Electrification could have a high potential for any machinery.76,77 Another approach is investing in producing renewable hydrogen as a heat source. Therefore, the above discussion has been considered for the production or supply action line in our roadmapping (Fig. 9).
BC's pulp and paper sector has taken initiatives toward reducing their emissions by adopting technology or process type innovations (shown in S2 in the ESI Material†). Developing renewable energies, such as biomass, geothermal, and heating pumps, and circular reuse of wasted high-grade heat, can support industries to use new low-GHG equipment and, importantly, the use of biomass as a feedstock for high-temperature production processes in both the cement78 and the pulp and paper industries.79 The projected deployment of hydrogen would create an estimated $100 billion industry for the fuel and associated equipment for BC sectors by 2030, reaching over $200 billion by 2050.45 Process emissions are also in the pulp and paper sectors. There is no other way to reduce process emissions except by capturing them.
In BC, Rio Tinto's aluminum facilities have taken the initiative towards reducing their emission by adopting novel technologies and processes. The aluminum metal provided from Rio Tinto's Kitimat Aluminum Smelter in BC (Fig. 5a) is an example of a nearly decarbonized facility, as the metal electrolysis is powered by BC Hydro's clean and near carbon-free electricity.82 Other decarbonization initiatives of Rio Tinto are shown in S3 in the ESI Materials.† While aluminum refining contributes to Rio Tinto's global emissions (Fig. 5b), BC's Kitimat Aluminum production facility is in a reasonably good position to achieve 100% decarbonization.
Fig. 5 (a) Rio Tinto Aluminum industry in the Northern part of BC. Image, Google Maps and RioTinto website. (b) The process contributing to Rio Tinto's global GHG emissions is demonstrated in the schematic. All rights reserved.24 |
BC has a competitive advantage in its innovative technologies, services such as digitization, considered in the roadmapping Knowledge and Capacity action line, Fig. 9, and policy expertise. While BC has a solid foundation in these areas, more can still be accomplished.85 Considering our findings in the result section, increased operational efficiency, electrification, and the utilization of renewable energy sources can create a carbon-free mining sector. The use of lithium batteries could aid mining decarbonization since BC and Canada already employ battery-electric technology for underground mining.86
The transition to a low-carbon economy creates increased demand for emerging commodities with new chemical properties that may enable innovative technologies. Fig. 6 shows BC mines, smelters, refineries producing copper, lead, zinc, and by-products, and advanced exploration projects87 targeting copper and zinc.68 While BC currently produces and processes most metals used in making solar cells, additional investments could sustain or expand the production of metals and minerals that convert solar energy to electricity.
Fig. 6 Mines, processing facilities, and advanced exploration projects associated with inputs for solar cells. Image source: adapted from Government of Canada (NRCan).87 |
With the addition of greenfield liquefied natural gas (LNG) facilities (such as LNG 1 and 2), BC's CO2 emissions will rise significantly. If these liquefaction facilities combust unabated natural gas (i.e., without CCU/S) when liquifying the gas for export, they would prevent BC from achieving its 2050 climate goals. If, however, they use electricity from zero-emission sources, they would have no impact on provincial GHG emissions and might contribute to some immediate reductions in global emissions by substituting for coal. Nevertheless, an opportunity does exist for the BC government to partner with this EITE industry to drive commercial hydrogen projects as part of the sector's net-zero agenda. As per our analysis, we estimated linear projections of the future cost of producing hydrogen from natural gas vs. from electrolysis from wind-based sources. There are many dynamics at play, for example, the price of natural gas could plummet as demand switches away from it, meaning that hydrogen from natural gas with CCU/S could potentially become cheaper. Also, if wind and solar are used to produce “green hydrogen” there are load factor issues for facilities that make it more expensive in many (but not all) situations – load factor being affected by the variability of both primary energy inputs. We evaluate this circumstance within the four lines of action in Section 3.4, and it is contemplated in our roadmapping in Fig. 9. Similarly, the chemical industry can move to adopt hydrogen as a feedstock with government support, as stated in the Hydrogen Strategy for Canada report in 2020.15
In the CleanBC roadmap report, BC is the first jurisdiction in Canada to set a specific sectoral target for reducing emissions from the oil and gas industry. The oil and gas sector contributes to 50% of industrial emissions in BC and 20% of the province's overall emissions.30 Still, the only petroleum refinery in BC, the Parkland Refinery Ltd, is one of the minor CO2 contributors compared with other EITE sectors such as pulp and paper and cement.
With high carbon capture rates in the oil and gas sector, it is estimated that the cost of producing blue hydrogen is $2.87 (US$2.09) a kilogram per tonne of CO2, while the cost of building green hydrogen is $4.99 (US$3.64) per kg with projections that it may come down to $2.55 (US$1.86) per kg.88
Digitalization is defined as using digital technologies, such as artificial intelligence (AI), big data technology, cloud technology, and robotics, to initially execute, control, and improve every tangible and intangible activity that together comprise the value chain,89 leading to the creation of intelligent products and services, and other business model transformations.90 Extensive research in the literature has shown that digitalization could contribute to reducing emissions in hard-to-abate EITE industrial sectors by transforming the entire value chain of the EITE industries.91,92 Cost reductions within the value chain of EITE industries could occur when technological innovations in one industry accelerate a series of process and product innovations in other sectors. Digital and AI technologies support and carry a powerful potential in this respect.93 Substantial GHG emissions reductions in hard-to-abate EITE industrial sectors can be achieved by embracing digital technologies.
Carbon capture and renewable hydrogen projects are still in the stage of Lab to Market, early commercialization and demonstration stages. Collaboration and partnerships between R&D academia and private institutions and companies must also be increased for hydrogen commercialization and scale-up, which could potentially reduce the costs associated with its value chain. Some transformative hydrogen and CCU/S technologies are still in the research lab or not yet invented. According to the International Energy Agency (IEA), this may account for nearly 50% of the technologies needed to meet our net zero global targets. For these nascent technologies, innovation and entrepreneurship training of STEM researchers can be a crucial component of accelerating solutions to market.54 Early-stage innovation supports are also needed to de-risk, shape and scale clean energy innovation.53,66
Electrification will play a major role in BC's EITE sector decarbonization in aluminum, mining, pulp and paper, and cement. There will be the continued need for metal and minerals to supply a future low-carbon and clean energy transition, and thus the mining and other metal and mineral production sectors also need to push towards net-zero carbon emissions by 2050. In this results section, we show that BC's near clean electricity grid, which is far ahead of most countries, offers BC the opportunity to shift industrial processes to nearly 100% clean electricity, using that energy to power manufacturing sectors and other industries like mining, minerals and forestry to produce low-carbon products. Therefore, the electrification has been considered in the four action lines within our roadmaping (Fig. 8 and 9).
When integrating any innovative technologies within existing EITE industrial sectors, it is important to consider that these energy intensive industries are highly dependent on incumbent infrastructure such as power grids, gas pipelines, and railways to supply energy and current feedstocks. A shift in any production processes is often constrained by the current infrastructure and requires new investment to transition.94 Individual companies and policymakers need to consider the cost implication of modifying the pre-existing infrastructure compared with newly developed infrastructure needed to support innovative technologies.
Fig. 7 Hydrogen production: Key Canadian Patent Assignee/Applicant, source: Authors' analysis based on data from Canadian Patents Database.99 |
Major Canadian oil and gas companies,100 such as Shell, Suncor Energy Inc. and Cenovus Energy Inc., down to small junior players based in Alberta, are highly interested in hydrogen production. These companies combined hold over 300 patents in hydrogen production.99
Electrolysis can achieve very low emissions if powered by renewable or nuclear energy. Solar power likely can achieve 1.0 kg CO2eq per kg H2 and wind 0.5 kg CO2eq per kg H2 in 2030, the difference resulting from the higher embedded Capex emissions for solar panels based on the projected 2030 scenario in IRENA's Global Renewables Outlook 2020 (ref. 41 and 99): 20% wind, 15% PV, 6% biomass, 15% hydro, 1% geothermal, 11% nuclear, 16% natural gas, and 16% coal. Electrolysis with run-of-river hydropower can achieve even lower emissions of 0.3 kg CO2eq per kg H2. Nuclear power achieves 0.6 kg CO2eq per kg H2, but it is also important to note that it leads to 0.115 g of radioactive waste per kg of hydrogen, based on spent nuclear fuel of 0.0021 to 0.0027 g kW−1 h−1 of electricity.
Capex-related emissions based on the global average grid mix of 66% renewable power in 2030 for asset manufacturing are very low across hydrogen production pathways. For fossil, nuclear, and most renewable power sources, Capex-related emissions are in the single-digit g CO2e per kW per h range and a low double-digit number in the case of PVs.101
(1) Demonstration projects for Carbon Capture and fully Renewable Hydrogen to target production, storage, and utilization goals by 2030.
(2) Increase investments in R&D activities related to innovative technologies and policies to incentivize support across new value streams to meet 2050 targets.
(3) Incorporate EITE industry infrastructure with on-site net-zero emission technology to handle production & delivery, leading to a rapid momentum for innovative technologies across EITEs.
(4) Develop a new revenue model for industries with an economic value proposition in lowering capital cost per unit of energy to accelerate the implementation of clean energy innovation.
The schematic in Fig. 8 emphasizes that all four action lines indicated on the Technological Roadmap (Fig. 9) must now be launched to achieve net-zero emission targets by 2050. BC's Hydrogen Strategy compares different hydrogen production methods based on the carbon intensity of each process.102 It also proposes regulating industry to have a maximum allowable carbon intensity that decreases over time. Assuming that the rate of decrease is in line with BC's emission reduction goals, then the question of how to produce the hydrogen becomes one of economics. To explore the hydrogen technology landscape in detail, it is necessary to evaluate different forms of hydrogen production, including their key technical components, materials, processes, innovations, and market development opportunities in the value chain for each EITE industry sector. Frost & Sullivan57 investigated the state of play of the electrolyzer market, discussing, among other topics, the role of technology service providers and recommended policies to stimulate innovation and R&D.103 Therefore, the above-stated actions have been considered in our technology roadmap analysis.
The “Roadmap Foundation-to-Action,” shown in Fig. 9, focuses on matching specific innovative technologies which EITE industries with an explanation of how these alternatives could be integrated. For example, clean hydrogen can be utilized to decarbonize several EITE sectors in BC, while also holding the potential to be a globally emergent and competitive clean energy transition industry. From this prioritization, we create a set of actions which are summarized and discussed in the upcoming sections.
Recognized as heavy industries in BC, oil and gas, cement clinker, pulp and paper mills, aluminum smelters, and the mining sector are the five largest CO2 emitters among BC resource-based and manufacturing industries (Table 2). However, they rank differently along the two dimensions generally accepted for assessing whether a sector is at risk of carbon leakage, i.e. carbon intensity and openness to national and international trade. Asymmetrical climate policies cause carbon leakage, that is, policies that impose carbon prices in one jurisdiction,2 in contrast to other jurisdictions that have no or less stringent climate policies and prices.104 The cement and pulp and paper sectors are very carbon-intensive but only moderately open to international trade, while aluminum and mining feature lower carbon intensity but higher trade openness. The pulp and paper sector accounts for over 2000000 tCO2e emissions and approximately 5% of total industrial energy consumption, contributing 2% of direct CO2 emissions from industries.105 Contributions of the Ore and Mineral and Manufacturing EITE sectors in BC towards GHG emissions can be found in Table 2.
The processes in each case that contribute to GHG emissions can be found in Table 1. There are several key components to consider in developing a clear pathway to achieve a low carbon-intensity economy, such as scaling up innovative technologies, rapidly bringing down their cost, investment priorities for specific technologies, the role of policies in creating demand for hydrogen, determining effective ways to produce hydrogen, determination and certification of quality and safety standards, and the development of hydrogen storage and transport, including blending hydrogen in natural gas pipelines.106,107
Decisions on green vs. blue hydrogen also have implications. For example, moving forward with green hydrogen requires the assumption that blue hydrogen infrastructure will eventually become stranded assets and that the cost of infrastructure modifications for the adoption of zero-carbon energy sources by EITE industries while taking into account the cost of green hydrogen production is predicted to decrease faster than blue hydrogen.44 This topic is discussed further in Section 4.3 and 4.4.
The schematic in Fig. 9 shows a technology roadmap and action pathways for EITE industrial decarbonization. The recommendations proposed in this roadmap could potentially help BC to identify a significant potential innovative technology to address a range of energy needs, along with opportunities for BC EITE industries to meet the demand for these innovative technologies and navigate its energy system transformation and pathway to decarbonize by 2050. With the need to address climate change and reach net-zero emissions, CO2 must be cut drastically from all areas of life, including EITE industrial sectors for which the emissions are challenging to abate. With increasing recognition that hydrogen, as one of the innovative technologies, could potentially play a key role in transforming these sectors, comes the challenge of deploying new technologies at scale to support the shift to a hydrogen economy.59
Fig. 10 shows the five EITE sectors' GHG emissions over 2020–2050 when implementing the innovative technologies, and policies recommended in our roadmap. From the data gathered and analyzed in this study, pathways with near-term GHG emissions are projected in line with BC government policies implemented until the end of 2025 and extended with comparable ambition levels by 2030, and beyond. As illustrated in Fig. 10, the decline in carbon intensity resulted from the fast deployment of innovative and renewable technologies across BC's EITE industrial sectors. As per our technological roadmap Foundation-to-Action (Fig. 9), renewable hydrogen meets 15% of BC growth in electricity demand. Solar, wind, and hydrogen generation each increased in the mid-term by around 55%, helping to avoid over 3 Mt in EITE sectors' emissions. All pathways (Fig. 8 and 9) assume immediate action is taken. GHG emissions for 2018–2022 were used to project the outcomes shown in Fig. 10.
Fig. 10 2050 pathway: emissions reduction potential by major abatement by technological roadmap. Source: Authors' analysis based on data from CEEDC. |
Our analysis was informed by the International Energy Agency (IEA). As the world's leading energy authority, the IEA36 is an authoritative resource providing governments with support and advice as they design and implement their roadmaps, and encouraging international cooperation across sectors to reach net-zero by 2050. Our analysis was also informed by innovation management literature, including technical economic analysis108,109 and input from Canadian cleantech accelerator Foresight CAC, which has been bringing BC's leading industries and cleantech entrepreneurs together in a “Core Cluster” initiative.42 A key component of Foresight CAC's Core Cluster innovation ecosystem framework is advising governments on policy-making.52 Our research team is actively collaborating with Foresight CAC, PICS, and BC government policymakers in recommending policies and solutions that can reduce BC's industrial GHG emissions and sustainably generate economic prosperity in the province. The innovative technology potential solutions required to meet BC net-zero 2050 goals are identified as being in the early stages of development. This roadmapping analysis provides potential recommendations to inform policy and actions taken within a near-term timeframe of 2025–2030.39,45,49,67,110,111
To achieve a net-zero emission economy by 2050, BC energy sources for industries must be largely decarbonized. This could impact hydrogen production pathway emissions.102 Most notably, electrolysis with grid electricity becomes viable compared to the 2030 global average grid mix, which remains carbon-intensive. Therefore, it has been included in Fig. 8 and 9.
Fig. 7 demonstrates electrolysis as the dominant green hydrogen production technology that existing companies are investing in patented research. While electrolysis needs further development regarding cost and implementation in most regions (the Hydrogen Council, published in January 2021 (ref. 113)), the case is much more compelling in BC due to the province's clean electricity grid.
Our analysis indicated that electrolysis + renewable electricity could potentially become viable compared to other production pathways by 2030. A cost comparison resulting from different methods of hydrogen production pathways is shown in Tables S8 to S11, in the ESI Materials.†102 TRL level, capital cost, production cost, and efficiency are also indicated. (Data source: adopted by the authors from Ajo Joseph, Frost & Sullivan55 and Abdin et al.102) To address the cost of hydrogen production, Tables S8–S11† provide information such as hydrogen cost and TRL level:
• Hydrogen storage: Energy Demand for Storing and Releasing Hydrogen, Global, 2020 (Table S8†).
• Hydrogen storage: Techno-economic Comparison of Liquefied Hydrogen Storage, Global, 2020 (Table S9†).
• Power-to-X technology: Technology Comparison, Global, 2020, 2020 (Table S10†).
• Alternative fuels production: Comparative Analysis, Global, 2019 (Table S11†).
The capital cost of green H2 production through low-temperature PEM electrolysis is estimated at 800–1000 $ per kW, while the high-temperature electrolysis is over 1000 $ per kW. Given these assumptions, renewable hydrogen produced through electrolysis is forecast to cost $2 per kg by 2050.
Operating and capital costs for hydrogen storage via ammonia is slightly lower than for liquid hydrogen (S9 in the ESI Material†),17,117 and ammonia has a high hydrogen density, which leads to low fuel consumption during transportation. Ammonia has good potential as a hydrogen carrier suitable for large-scale storage and transport. However, due to insufficient technical maturity, ammonia cracking is the main obstacle to implementing the ammonia hydrogen storage cycle.118,119 Thus, another alternative in BC is to produce methanol, allowing BC to become a significant methanol production centre that would be an excellent use of large quantities of green hydrogen. Therefore, it is contemplated in the Market Development Demand action line in Fig. 9.
Producing methanol from green hydrogen could potentially put an extra load on the electricity grid and is a constraint that must be considered. BC could potentially generate the electricity required for industrial quantities of green hydrogen49 on top of all the electricity needed for industrial heat pumps and the other added loads of the future clean economy. This is an essential question since BC Hydro has predicted that in approximately ten years, BC will only be able to provide for some of the anticipated demand for electricity.49
Wind and solar may provide sufficient green and clean future energy. Still, there is no single set of solutions about what to do with this renewable energy when demand and supply are out of sync in time and location. A single-dimensional approach (e.g., batteries alone or a renewable hydrogen economy) has a lower chance of success. Ammonia and hydrogen are two complementary zero-carbon fuels with good potential to replicate the immense fuel reserves and usage that fossil fuels provide us with today.115 To spur industries to accelerate, Foresight CAC, PICS, and Simon Fraser University have provided programs as motivation and guidance.1,42
The leading decarbonizing technologies for producing hydrogen feedstock in ammonia/methanol are:
(1) Keeping steam methane reformed-produced hydrogen with natural gas as a feedstock, but adding CCU/S or carbon dioxide pyrolysis processes to produce solid carbon.
(2) Fuel switch to biomass-based hydrogen. Biomass is a possible scalable feedstock, i.e., in the pulp and paper sector; or
(3) switch to green hydrogen electrolysis.
The experimentation with pilot projects and decisions to invest in any of these alternatives must be made in the context of constraints on clean electricity supply and prioritization of energy demand in BC. Thus, all these promising alternatives for decarbonizing EITE industries have been included in our customized technology roadmap, shown in Fig. 9.
The facilities developed by Carbon Engineering captures CO2 directly from the air and stores it safely, permanently, and securely underground in geological formations. With DAC, atmospheric CO2 can also be used as a feedstock to create low-carbon products like plastics and concrete.121 Carbon-capture technologies based in BC and Canada, categorized by technology and process type, description, state of development, GHG impact, energy impact, cost, and references are listed in S6 in the ESI Material.†
Decarbonizing emissions from process heat, for example, a total of 20 MtCO2e in the Aluminum industry at Rio Tinto in BC, can be a part of BC's solution. A low-carbon energy system could involve a possible combination of measures including a significant decarbonized heating process. To decarbonize heat, the BC government announced a policy to cap emissions from the gas distribution system, a mandate to require 100% efficient heating equipment in future sales, and an intention to support infrastructure electrification financially and institutionally.4 If low-carbon fuel may not play a significant role in heat decarbonization, decision-makers might explore alternative applications for biomethane and hydrogen in other hard-to-abate sectors. It is reported by Stark et al.,66 R&D in zero-carbon heat technologies is needed to increase attainable top temperatures, reduce capital costs, and in the case of solar thermal, increase resource dispatchability. This could achieve low cost, energy, and GHG emissions trade-offs of the various solutions with zero-carbon heat.
Electrification has significant potential as a world-leading strategy under varying stages of research from R&D labs to market and scale-up85 contributing towards a 2050 net-zero emission target. Electrification is realized through the installation of industrial heat pumps and electric vehicle chargers., i.e. in the mining sector. Direct government financial support can also accelerate electrification. For example, the BC Government's CleanBC plan includes discounted industrial electricity rates with about $20 million in other incentives.77 Increased operational efficiency of electrification is particularly advantageous in mining sectors that are difficult to decarbonize and where alternatives are limited. Advances in lithium batteries will decarbonize the mining sector for vehicle use underground and BC is already a leader in battery-electric technology for underground mining.86
Innovative technologies, such as electrification, replacing fossil fuels with sustainably produced biomass, and low carbon-intensity hydrogen, are available to decarbonize industry, and their adoption can be accelerated by innovation policy and climate policy. As different types of hydrogen production are not equal in achieving GHG emission targets by 2050, our technological roadmap provides recommendations to advance zero-carbon and renewable hydrogen pathways, with a particular focus on lowering the price of green electricity and thus leveraging hydropower in BC is critical to achieving this goal.49 Nevertheless, despite low-to-zero carbon pathways for hydrogen production, adopting CCU/S technologies can be applied to other production pathways with regulated carbon-intensity limits to be established within the hydrogen value chain in the near and short-term.
(1) R&D funding: align with net-zero targets prioritizing a strategic investment fund to support the below recommendations,109,112,125 including BC's five EITE sectors, supporting the industry through establishing dedicated R&D funding and the challenges of modifying existing EITE infrastructures.127,128 Examples include BC's renewable/net-zero emission energy program and federal funding through Natural Resources Canada (NRCan).
(2) Stimulate R&D interactions between different sectors within the value chain, and apply funding to overcome financial barriers to achieve feasibility demonstration and early-stage commercialization for innovative technologies with high unit costs.8,128
(3) Provide investment support and corporate tax provisions to aid private companies' R&D activities and capital costs, i.e. with government support, cleantech-based project funds annually to 2030.129–131
(4) Invest funds for cleantech-based projects with industrial infrastructure and energy-scale modification126,127 to support heat decarbonization, including electrification, digitalization, and sustainability86,132–134 of processing systems in EITE sectors to realize cost savings in industrial processes.135,136
(5) Modify EITE industry infrastructure with on-site net-zero emission technology to handle production and delivery, leading to a rapid momentum for innovative technologies in EITE sectors, supported across new value streams to meet net-zero targets.
(6) Targeted funding to fill knowledge gaps surrounding hydrogen or hydrogen-blended gas distribution and transmission to end-use applications.15,106
(8) Require CCU/S deployment, reducing fossil fuels CO2 emissions in 2025.139,140
(9) Develop a continuum of supports to bridge fundamental research to clean energy innovations that lower emissions and/or lower cost, including innovation training and fellowships for STEM researchers, de-risking supports, and pre- and post-venture formation commercialization supports.
(10) Update regulations and incentives for conventional gas-supply equipment for end-users of EITE industries to incentivize industrial building improvements and retrofits such as high-efficiency heat pumps.33,59
(11) Implement the 2023 Canada federal budget96 supporting technology development and investment tax credits effective with a current annual investment of $15–25 billion131
(12) As per the 2023 Canadian federal budget, introduce a new refundable Clean Hydrogen Investment Tax Credit up to a maximum rate of 40% to attain net-zero emissions in Canada.96 Verification of low carbon intensity claims might be necessary.
(13) Advance a coordinated strategy and roadmap for implementing CCU/S and negative emissions technologies in all difficult-to-abate industrial processes16,140,141 through infrastructure modifications.126,127,142
(15) Blue hydrogen (fossil fuel-derived hydrogen with CCU/S) is forecast to lose its cost advantage relative to green hydrogen from electrolysis in the coming decade due to innovative support of hydrogen produced from electricity.44
(16) Commercial demonstration projects of low-carbon technologies should be fully developed and constructed. Such projects should focus on reductions in industrial process emissions using CCU/S and direct air capture, and implementing bioenergy and hydrogen applications in energy-intensive industries.67
(17) Electrification of mechanical and chemical processes, and zero emissions heating within the pulp and paper,95 cement,143 oil and gas,100 mining,68 aluminium,82 and metal (i.e., copper/lead/zinc) smelting sectors should be realized by 2030.68
(18) Ensure that major CCU/S projects in BC are scoped to reduce CO2 emissions by >3 million tonnes annually by 2030 to achieve targets.33,144
(19) Support CCU/S projects to decarbonize methanol and ammonia production145 and prepare processes to convert to green hydrogen when cost-competitive.
(20) Ensure that methane emissions from the oil and gas sector can be reduced by over 75% from 2020 to 2030.54,146
(22) Implement technology requirement policies, zero-emission source building code materials for embodied emissions or technology standards-setting minimum requirements for energy efficiency, fuel economy, emission limits and carbon intensity by 2035.148,149
(23) Complete BC's entire decarbonization of the electricity sector by 2035 to enable net-zero emission electrification of industrial processes as applicable.149
(24) Realize full decarbonization of oil and gas, pulp and paper, mining and cement industries, where emissions associated with chemical processes that cannot be eliminated with existing or near commercialized technologies require far greater scaling of hydrogen, Li-batteries, CCU/S,55 heat pumps,150 and biofuels.151
(25) Realize full integration of net-zero emission hydrogen, ammonia, and methanol as energy carriers and industrial feedstocks, as a chemical feedstock for ammonia, methanol, food and drug production, as well as oil and gas sector processing used in crystal growth, glass manufacturing, chemical tracing, metal fabrication, polysilicon and semiconductor manufacturing, metal production, and thermal processing.30
(26) Support full electrification of hydrogen produced from renewables-based electrolysis by 2050.108,152
To aid public and private sectors in striving for meaningful and clear pathways to decarbonization, we have developed a Technology Roadmap for BC to achieve climate targets in 2050 while enabling economic development. The need for more decarbonization technologies both provincially and globally is rising, and the need for efficient, reliable, and scalable production processes is a crucial factor. Although long-term demand for renewable hydrogen production and CCU/S technologies is apparent, an accelerated pathway to address this demand is needed by designing industrial technologies with low-cost processes, productivity, and facilitating market opportunities arising from the scale up of industrial processes for existing stakeholders within the value chain. BC companies and research institutes can potentially create a competitive advantage in utilizing green hydrogen technology. Our technology roadmap depicts how BC could develop this hydrogen sector to address environmental and economic goals. BC and Canadian government policymakers have an opportunity to shape the development of the future operations and supporting infrastructure of EITE industries to accelerate a transition to net-zero emissions and generate the foundation for a higher economic value proposition.
Calculating emissions and costs for energy production presents a challenge for deciding how to account for the type of energy usage, technology, and products within our studied five EITE sectors. These detailed emissions, from each energy resource, were not extensively calculated in this study, given the varying stages of technology development and decarbonization policies and capacity change in EITE industries. For example, future research could include an additional sensitivity where the production costs of biomethane or hydrogen decline over time as technologies improve.
It was beyond the scope of this study to conduct a full sensitivity analysis on the many different parameters such as the emissions intensity and trade intensity of the five EITE industries studied. Future research could incorporate conducting a full energy-economy-emissions modelling analysis, which would assess key quantitative indicators such as the turnover rate of existing technology stock with zero-emissions alternatives, the cost of emissions abatement, changes to emissions and energy intensity of abating sectors, and the extent of trade exposure of EITE industries and the limits to emission abatement without the support of government policy. A full quantitative analysis would assess the impact of these aforementioned indicators with the implementation of different policy options in BC and Canada. While this study did not conduct a full energy-economy-modelling analysis, our research will enable future quantitative analysis by providing modellers with a timeline and development steps of technological innovation, expected uncertainties in the market adoption of zero-emissions technologies, and prescribed decarbonization trajectory necessary to attain GHG emissions targets while providing sufficient process and unit cost reductions to enable BC and Canadian EITE industrial firms to continue exporting globally. Furthermore, even without additional modelling analysis, the results of our work may be useful to policymakers planning for the clean energy transition and ensure that energy systems remain affordable and reliable amidst their decarbonization trajectory.
AI | Artificial Intelligence |
BAT | Best Available Technology |
BC | British Columbia |
CCU/S | Carbon Capture and Utilization/Storage |
CICC | Canadian Institute for Climate Choice |
CSPC | Canadian Science Policy Conference |
CO2 | carbon dioxide |
ECCC | Environmental and Climate Change Canada |
EITE | Emissions-Intensive and Trade-Exposed |
FBMR | The Fluidized Bed Membrane Reactor |
GHG | Greenhouse gas |
IEA | International Energy Agency |
IPCC | The Intergovernmental Panel on Climate Change |
IRENA | International Renewable Energy Agency |
kg | kilogram |
LNG | Liquefied Natural Gas |
OECD | The Organisation for Economic Co-operation and Development |
PV | photovoltaic |
PEM | Proton Exchange Membrane |
R&D | Research and Development |
SCM | Supplementary Cementitious Materials |
SDTC | Sustainable Development Technology Canada |
SMR | Steam Methane Reforming |
tCO2e | tonne of CO2 equivalent |
Tcf | trillion cubic feet |
TRL | Technology Readiness Level |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d3su00335c |
This journal is © The Royal Society of Chemistry 2024 |