Resource Demand of Pathways towards Electric Mobility ...Boron magnet replaced by electrically...
Transcript of Resource Demand of Pathways towards Electric Mobility ...Boron magnet replaced by electrically...
Based on project “Global Perspectives and Life Cycle Assessment of Electro Mobility - STROM Assist”
Resource Demand of Pathways towards Electric Mobility: Analyzing material demand, critical resources and emissions
World Resources Forum, Davos, 13 October 2015 Katrin Bienge Project Team: Ole Soukup, Peter Viebahn, Katrin Bienge, Michael Ritthoff
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Global Perspectives and Life Cycle Assessment of Electro mobility (STROM – Assist)
DLR – German Aerospace Center e.V. Wuppertal Institute for Climate, Environment and Energy
DLR Institute for vehicle concepts
DLR Institute for transport research
Wuppertal Institute
Client: German Federal Ministry of Education and Research (BMBF)
Duration: Oct 2011 - Mar 2015
Aim (WP4): Material Intensity Analysis: Identifying material demand for the introduction of e-mobility in Germany (and worldwide) and depicting potentially conflicting goals
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Material Intensity Analysis Objectives
Overarching objective: Identifying resource intensity for the introduction of e-mobility in Germany (and
worldwide) and depicting potentially conflicting goals
Sub-Objectives: Identifying resource intensity of individual electric vehicles and of conventional
vehicles, and comparing them
Scenarios as frameworks for calculating and projecting material requirements in Germany (and worldwide)
Recommendations regarding future support measures for the introduction of e-mobility
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Material Intensity Analysis Method
Three methods for assessing cumulated material demand:
MIPS-Method („Material-Input per Service-Unit“) for system analysis: “Material intensity“ as ecological indicator of resource use across the life
cycle (incl. “material rucksacks“)
Identifying “critical“ materials, where availability or environmental hazard at extraction may threaten set extraction targets
Identifying Global Warming Potential for system analysis: GHG emissions as ecological indicator of climate impact across the life cycle
(incl. “GHG rucksacks“)
Nd? Dy?
Li?
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Material Intensity Analysis Method and Approach
Approach Identifying material inventories per system component, including a targeted analysis of
critical raw materials and material losses
Linear scaling according to weight of components
Identifying material requirements (Material Footprint) and emissions (GWP)
ICE-B Combustion Gasoline
Middle Segment MPT
ICE-D Combustion Diesel
ICE-CNG Combustion Nat. Gas
HEV-B Hybrid Gasoline
PHEV20 Plugin-Hybrid
BEV Battery-electric
REEV80 Range Extender
FCEV Fuel Cell
Object of study Reference segment: middle segment of
motorized private transport (MPT), GER
Drive concepts: ICE-B, ICE-D, ICE-CNG, HEV-B, PHEV20, REEV80, BEV, FCEV
Life cycle phases: production, use, end of life
Service unit: kg/component or vehicle
Period of time: 2010, 2020, 2030 (until 2050)
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Material Intensity Analysis Basic assumptions for vehicle analysis
Technological development: e.g. market share of electric machine types (permanently excited synchronous machines -PSM- based on Neodymium Iron Boron magnet replaced by electrically excited asynchronous machines -ASM- without rare earth metals: ASM: 15 % from 2030 und 25 % from 2040); e.g. Lithium-Ion battery (no change in technology due to missing LCI data of 4th generation Li-sulphur or Li-air)
Weight reduction: from 2010 to 2030 (beyond 2030 constant) Energy (use phase): reduction from 2010 to 2020 (beyond constant); hydrogen
production process based on steam reformation of natural gas replaced by alkaline electrolysis after 2030
Energy mix: based on existing scenarios with increasing share of renewable energy
No replacement of system components Use phase: 10 years and 150.000 km
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Material Intensity Analysis Comparing drive concepts and their direct material input
Comparing electric drive concepts across time and in the production phase Material demand per system component in 2010
Drive concepts of e-mobility
Mat
eria
l dem
and
(kg/
com
pone
nt)
Fuel Cell
Battery
Power Electronics
ICE engine
Rest of Drivetrain
Harness
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Material Intensity Analysis Abiotic Material Requirements of Vehicles (Material Footprint)
Comparison of abiotic Material Demand of drive concepts across time from a life cycle perspective (per year)
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Material Intensity Analysis Global Warming Potential of Vehicles
Comparison of global warming potential of drive concepts across time from a life cycle perspective (per year)
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Material Intensity Analysis Abiotic Material Requirements at Scenario Level
Definition of transport scenarios for Germany
STROM-min STROM-mid (NPE)
Strom-max
Number of cars (Tremod 2012 basis)
42 mil. (2010-2050) 42 mil. (2010-2050) 42 mil. (2010-2050) no ICE- Gasoline, ICE-Diesel until 2050
Number of electric vehicles (PHEV20, REEV80, BEV)
0,1 mil. (2020) 1 mil. (2030) 2 mil. (2040) 3 mil. (2050)
1 Mio. (2020) 6 Mio. (2030) 11 Mio. (2040) 16 Mio. (2050)
1 mil. (2020) 12,6 mil. (2030) 19 mil. (2040) 25,3 mil. (2050)
Number of FCEV 0 (2020) 0 (2030) 0 (2040) 0 (2050)
0 (2020) 1,4 mil. (2030) 2,4 mil. (2040) 3,1 mil. (2050)
0 (2020) 4,2 mil. (2030) 6,3 mil. (2040) 8,4 mil. (2050)
Graph
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Material Intensity Analysis Abiotic Material Requirements and GWP at Scenario Level (Germany)
Results: Abiotic material requirements and GWP of scenarios (cumulated, example: Germany) Production, use and disposal of all vehicles in the period 2011-2050 in Germany with
supply of electric drive energy based on BMU 2012, Scenario 2011 A:
Abiotic material intensity of MPT in Germany based on scenarios (2011-2050, only cars)
GWP of MPT in Germany based on scenarios (2011-2050, only cars)
Use, conventional vehicles
Use, electric vehicles (energy mix BMU 2012, Scenario 2011 A
Production
EOL/Disposal
Use, conventional vehicles
Use, electric vehicles (energy mix BMU 2012, Scenario 2011 A
Production
EOL/Disposal
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Material Intensity Analysis Assessing Criticality
Assessing 11 elements: silver, gold, gallium, indium, germanium, tantalum (used in power electronics and other electronic devices), platinum, palladium (being predominant in the exhaust gas catalytic converter), lithium (battery), neodymium, dysprosium (permanent magnets of electric engines).
Criticality and Use of Elements
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Material Intensity Analysis Assessing Criticality
Results: Demand for raw materials of scenarios, example: Dy
Cumulated demand (2011-2050) for Dysprosium of MPT in Germany in different scenarios(only cars)
Cumulated demand (2011-2050) for Dysprosium of MPT worldwide in different scenarios(only cars)
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Material Intensity Analysis Assessing Criticality
Example: Rare earths – Dy, Tb
Other countries
Reserves of rare earths are distributed across few countries
Europe has no reserves, but resources
Rare earths have to be assessed in a differentiated way according to Elements (e.g. in many extraction areas of SEE high share of Nd, but low share of Dy)
Critical demand: strongly exceeds the assumed limits of one annual extraction in all scenarios (390% – 3,130% in case of Germany, 196% - 845% globally) and that one of the reserves in all German scenarios (0.1% – 1.2%) and in most global scenarios (10% – 44%).
Greenland
India
Former Soviet Union
D; ca. 5,2 kt
World; ca. 142 kt
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Material Intensity Analysis Results and Recommendations
Conflicting goals – climate and resource protection: Large share of electric vehicles in future fleets may contribute to GHG-reduction, but the needed additional components are characterized by high material intensity.
Criticality: In relation to worldwide reserves, scenarios with high market penetration of electric vehicles show a high demand for specific raw materials (e.g. Li, Dy).
Recommendations (selection): Prevent scarcities: Dy-demand should drastically be reduced and Li-recycling advanced; R&D for recycling of Nd and Dy: timely availability of infrastructure and technology
Select technologies for minimized use of critical resources during product development; Dilemma: short-term competitive disadvantage (expensive materials), but long-term advantage (avoiding price shocks)
Material Input: Recycling to reduce extraction of primary raw materials; Substituting materials (however, material requirements of Glider can hardly by reduced by substitutes); Recycling-friendly production (e.g. with homogeneous materials); Reducing scrap
More intelligent use patterns / mobility and better utilization of vehicles
Thank you for your attention!
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Material Intensity Analysis MIPS method
Up-stream material flows
Life-cycle material inventory (production, processing, use, etc.)
Emissions (e. g. CO2, CH4, NOx, hazardous waste etc.)
Impact Assessment (e. g. Global Warming Potential)
Output
MIPS
LCA
Abiotic Resources
Biotic Resources
Water
Air
Translocation of soil
Unused extraction
Source: WI
While LCA usually consider abiotic depletion, MIPS (material input per service unit) also includes the economically unused extraction (and further categories).