Electric Bicycle
TransportationCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 0 | 0% | |
| Scope 2 | 7.2 | 15% | |
| Scope 3 | 40.8 | 85% | |
| Total | 48 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| aluminum frame production | S3 | 42% |
| lithium-ion battery material extraction and processing | S3 | 28% |
| electricity consumption during use | S2 | 15% |
| motor and component manufacturing | S3 | 10% |
| transportation and distribution | S3 | 5% |
Manufacturing Geography
- Region
- China
- Grid Intensity
- 555 gCO2/kWh (IEA 2023)
Material Composition Assumptions
Electric bicycles incorporate several resource-intensive materials that drive their carbon footprint. The aluminum frame serves as the primary structural component, typically weighing 2-3 kilograms and representing approximately 15% of total product weight. Lithium-ion batteries contain multiple critical minerals including lithium, cobalt, and nickel, with battery packs weighing 2.5-3.5 kilograms and comprising roughly 18% of product mass.
Steel and stainless steel components account for drivetrain parts, fasteners, and structural elements, contributing about 3-4 kilograms or 20% of weight. Copper and graphite materials within battery electrodes add specialized functionality while plastic housings protect electrical components and cables. Rubber tires complete the material profile, with the remaining mass distributed across smaller electronic components and motor assemblies.
Manufacturing Geography
Electric bicycle production concentrates heavily in China, which supplies approximately 85% of global electric bicycle manufacturing capacity. Chinese facilities benefit from established supply chains for both aluminum processing and lithium-ion battery production, creating manufacturing efficiencies but also exposure to carbon-intensive electricity grids.
The regional grid intensity of 555 gCO2/kWh significantly influences manufacturing emissions, particularly for energy-intensive processes like aluminum smelting and battery cell production. This grid composition relies substantially on coal-fired power generation, elevating the carbon footprint of upstream manufacturing activities compared to regions with cleaner electricity sources.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 555 gCO2/kWh | 48 | Baseline |
| European Union | 275 gCO2/kWh | 42 | -12.5% |
| United States | 400 gCO2/kWh | 45 | -6.3% |
| South Korea | 450 gCO2/kWh | 46 | -4.2% |
| Taiwan | 500 gCO2/kWh | 47 | -2.1% |
Provenance Override Guidance
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Submit aluminum frame manufacturing location with regional electricity grid carbon intensity documentation and smelting process energy consumption data.
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Provide lithium-ion battery cell production facility location, capacity specifications, and material sourcing regions for lithium, cobalt, and nickel extraction.
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Document motor and drivetrain component manufacturing origins with supplier-specific energy usage and transportation distance calculations.
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Supply end-of-life battery recycling program participation rates and material recovery percentages for closure of material loops.
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Provide actual electricity consumption measurements during manufacturing operations with time-stamped grid intensity data for production periods.
Methodology Notes
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The CCI score represents cradle-to-gate emissions covering material extraction, manufacturing, and distribution to retail locations, excluding operational use and end-of-life disposal.
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Scope 3 emissions dominate due to aluminum frame production and battery material processing, which occur upstream from final assembly facilities.
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The functional unit assumes a standard electric bicycle weighing approximately 20 kilograms with 400-500 watt-hour battery capacity.
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Transportation emissions reflect typical shipping distances from Asian manufacturing hubs to North American and European markets.
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Battery degradation and replacement cycles are excluded from the current methodology, though future versions may incorporate multi-year operational assessments.
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Charging infrastructure and electricity grid emissions during consumer use fall outside the current CCI boundary but represent significant lifecycle considerations.
Related Concepts
Sources
- European Cycling Federation 2011, 2015 — Quantified lifecycle emissions comparing electric and conventional bicycles across European markets.
- Del Duce et al. 2011, Life Cycle Assessment of Conventional and Electric Bicycles — Established manufacturing as the dominant contributor to electric bicycle carbon footprints.
- McQueen et al. 2020, Transportation Research Part D — Analyzed replacement patterns showing electric bicycles displace more car trips than conventional models.
- Cherry 2007, Environmental Impacts of E-Bikes in Chinese Cities — Documented grid intensity variations affecting operational emissions across different electricity sources.
- BikeRadar 2025, Cycling Environmental Impact Analysis — Measured typical energy consumption rates for electric bicycle charging and usage patterns.
- Polytechnique Insights 2024, Carbon Footprint of Electric Bikes — Evaluated battery recycling programs achieving high material recovery rates from end-of-life units.