- •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 policy and stakeholder actions |
7. Enabling policy and stakeholder actions
As the preceding analysis has illustrated, material efficiency strategies have the potential to play an important role in achieving global emissions reduction objectives. Various challenges will need to be overcome to ensure effective use of materials, including barriers related to cost, delivery times, behaviour, lack of awareness and the regulatory environment. The combined efforts of governments, industry, the research community and society will be needed to overcome these challenges and accelerate the efficient use of materials.
Challenges and costs of material efficiency
Without any incentive or requirements to pursue material efficiency, or explicit demand from consumers, designers and manufacturing or construction companies may be unaware of the possible benefits of material efficiency; or they may chose not to pursue material efficiency due to real and perceived risks, financial costs or lost revenues and time constraints. In some cases, fragmented supply chains may present challenges for achieving material efficiency, such as when users or demolition contractors are not connected to construction companies to facilitate end-of-life reuse of materials. The regulatory environment may also restrict pursuit of material efficiency, such as when prescriptive design standards prevent uptake of new materials or design methods.
An in-depth cost assessment was not part of this analysis. Further analysis will be required to assess to what degree material efficiency would be more cost-effective than other options to reduce emissions, such as carbon capture and uptake of alternative fuels. A recent circular economy analysis by Material Economics indicates the relative cost of many of the strategies examined in the present analysis (Material Economics, 2018). It suggests that considerable potential exists to reduce emissions through material efficiency while achieving savings in financial costs. Strategies with negative abatement costs include car-sharing, reducing waste in buildings construction and increasing collection rates of aluminium. Strategies that account for a considerable portion of material demand reduction in the Clean Technology Scenario are estimated to have positive although moderate costs, such as EUR 50 (euros) per tonne (t) of carbon dioxide (CO2) abated for buildings reuse and EUR 60/t for reducing steel fabrication losses. Other strategies that account for a substantial portion of the additional material demand reductions in the Material Efficiency variant are at the higher end of the cost curve, such as EUR 85/t abated for material efficiency in buildings design and construction and EUR 100/t for vehicle lightweighting. All strategies in the Material Economics analysis have abatement costs no higher than EUR 100/t. This suggests that while costs of material efficiency may not be negligible in all cases, they are likely to fall within a reasonable range of what will be necessary to achieve low-carbon transition objectives. Thus, in the short term, it would be advantageous to begin pursuit of the lower cost strategies, while also starting to prepare for implementation of a broader range of strategies in the medium to long term.
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