- •Material efficiency in clean energy transitions
- •Abstract
- •Highlights
- •Executive summary
- •Clean energy transitions require decoupling of economic growth from material demand
- •Further ambitions on material efficiency can reduce deployment needs for low-carbon industrial process technologies and achieve emissions reduction throughout value chains
- •Policy and stakeholder efforts are needed to improve material efficiency
- •Findings and recommendations
- •Policy recommendations
- •Historical demand trends for materials
- •Enabling strategies to move towards more sustainable material use
- •Implications of deploying further material efficiency strategies
- •Material demand
- •Steel
- •Cement
- •Aluminium
- •Energy and CO2 emissions
- •Buildings construction value chain
- •Vehicles value chain
- •Enabling policy and stakeholder actions
- •Technical analysis
- •1. Introduction
- •2. Historical demand trends for materials
- •References
- •3. Enabling strategies to move towards more sustainable material use
- •Material efficiency strategies
- •Design stage
- •Fabrication or construction stage
- •Use stage
- •End-of-life stage
- •References
- •4. Implications of deploying further material efficiency strategies
- •Material demand outlook by scenario
- •Steel
- •Cement
- •Aluminium
- •CO2 emissions and energy implications of material efficiency
- •References
- •5. Value chain deep dive #1: Buildings construction
- •Material needs across the buildings and construction value chain
- •Material efficiency strategies for buildings
- •Outlook and implications for steel and cement use in buildings
- •References
- •6. Value chain deep dive #2: Vehicles
- •Material needs of vehicles
- •Material efficiency strategies for vehicles
- •Outlook and implications for vehicle material use and life-cycle emissions
- •EV battery materials
- •Battery materials supply
- •CO2 emissions from battery production
- •Battery recycling
- •References
- •7. Enabling policy and stakeholder actions
- •Challenges and costs of material efficiency
- •Policy and action priorities
- •Increase data collection, life-cycle assessment and benchmarking
- •Improve consideration of the life-cycle impact at the design stage and in CO2 emissions regulations
- •Increase end-of-life repurposing, reuse and recycling
- •Develop regulatory frameworks and incentives to support material efficiency
- •Adopt business models and practices that advance circular economy objectives
- •Train, build capacity and share best practices
- •Shift behaviour towards material efficiency
- •References
- •General annexes
- •Annex I. Reference and Clean Technology Scenarios
- •Annex II. Energy Technology and Policy modelling framework
- •Combining analysis of energy supply and demand
- •ETP–TIMES supply model
- •ETP-TIMES industry model
- •Global buildings sector model
- •Modelling of the transport sector in the MoMo
- •Overview
- •Data sources
- •Calibration of historical data with energy balances
- •Vehicle platform, components and technology costs
- •Infrastructure and fuel costs
- •Elasticities
- •Framework assumptions
- •Technology approach
- •References
- •Annex III. Material demand and efficiency modelling
- •Overview of material demand modelling methodology
- •Buildings value chain assumptions and modelling methodology
- •Vehicles value chain assumptions and modelling methodology
- •Transport infrastructure value chain assumptions, modelling methodology and preliminary findings
- •Material intensity of transport infrastructure
- •Rail
- •Roads
- •Material use in transport infrastructure in the RTS and CTS
- •Material efficiency strategies for transport infrastructure
- •References
- •Annex IV. Transport policies assumptions and impact on activity levels
- •References
- •Abbreviations, acronyms, units of measure and regional definitions
- •Abbreviations and acronyms
- •Units of measure
- •Regional definitions
- •Acknowledgements
- •Table of contents
- •List of figures
- •List of boxes
- •List of tables
Material efficiency in clean energy transitions |
Enabling strategies to move towards more sustainable material use |
3. Enabling strategies to move towards more sustainable material use
With expected population and economic growth over the coming decades, the Reference Technology Scenario (RTS) sees world demand for steel grow by approximately 30%, cement by 10% and aluminium by about 75% through to 2060, relative to 2017 levels.4 The expected future trends differ from observed trends in the past two decades, which saw large increases in cement and steel demand, primarily due to rapid growth in the People’s Republic of China (“China”).
While a substantial portion of the growth in material production was necessary to facilitate infrastructure development and subsequently economic growth, the rise in production capacity was higher than the growth in domestic demand. This resulted in overcapacity and lowered utilisation rates, particularly for cement, which has a limited potential for trade. The growth in cement and steel production in China is now levelling off. It is predicted that economic development in other regions will result in more moderate growth in demand for cement and steel. Expected shifts in applications (e.g. lightweighting of vehicles under current trends and growth in consumption of electric devices) may result in considerable increases in aluminium demand. Together, the increasing future material demand trajectories pose challenges for sustainability.
Materials demand and production need to be managed to reduce the impact on natural resources, air, water and the climate. Reducing the impact of materials is the foundation of the United Nations Sustainable Development Goal 12: ensure sustainable consumption and production patterns (United Nations General Assembly, 2015). The goal includes a target (target 12.2) to achieve the sustainable management and efficient use of natural resources by 2030. This is measured in terms of the material footprint, which is the amount of primary materials needed to meet a country’s needs, and domestic material consumption, which is the amount of natural resources used in economic processes. The goal also aims to substantially reduce waste generation through prevention, reduction, recycling and reuse (target 12.5). However, economic development is also needed to achieve the Sustainable Development Goals. As the preceding chapter has shown, material demand and its associated effects have historically coincided with economic growth. Thus, there is a need to decouple economic growth from a combination of demand for materials and the environmental impact of materials production, to enable achievement of development objectives while ensuring sustainability.
The environmental impact of materials depends on the impact per unit of material produced and the quantity of materials consumed. Looking specifically at carbon dioxide (CO2) emissions, the emissions per unit of material can be reduced by improving the production processes of a given material. This includes switching to lower-carbon fuels, improving energy efficiency and shifting to innovative low-carbon production processes, or switching to different materials with lower production emissions. The quantity of material demanded can be reduced by employing various material efficiency strategies, which aim to lower material consumption without reducing the quantity or quality of services provided. Other factors, such as technological shifts to help mitigate climate change, can also affect the quantity of materials demanded. Thus, the
4 RTS material demand projections are based on historical demand trends, observed material demand saturation levels, and population and gross domestic product projections.
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