AA Rechargeable Battery
ElectronicsCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 2.24 | 8% | |
| Scope 2 | 4.2 | 15% | |
| Scope 3 | 21.56 | 77% | |
| Total | 28 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| Raw material extraction (nickel, rare-earth metals) | S3 | 42% |
| Battery manufacturing and assembly | S2 | 28% |
| Transportation and logistics | S3 | 18% |
| Recycling and end-of-life processing | S3 | 10% |
| Direct process emissions (thermal processes) | S1 | 2% |
Manufacturing Geography
- Region
- China
- Grid Intensity
- 555 gCO2/kWh (IEA 2024)
Material Composition Assumptions
This assessment covers nickel-metal hydride rechargeable batteries with standard AA dimensions. The primary electrode material consists of nickel oxide hydroxide cathode weighing approximately 8 grams, representing 32% of total battery mass. The hydrogen-absorbing alloy anode contains nickel and rare-earth elements including lanthanum, cerium, and neodymium, totaling 6 grams or 24% by weight. Steel casing and terminals contribute 7 grams at 28% of mass. Potassium hydroxide electrolyte accounts for 2.5 grams representing 10% of composition. Additional components include tetrafluoroethylene binder and nickel mesh separator materials totaling 1.5 grams or 6% of the 25-gram battery weight.
Manufacturing Geography
China dominates global rechargeable battery production, accounting for approximately 70% of worldwide NiMH battery manufacturing capacity. The assessment assumes Chinese manufacturing with grid electricity intensity of 555 grams carbon dioxide equivalent per kilowatt-hour. This carbon-intensive energy mix significantly influences Scope 2 emissions from battery assembly operations, thermal processing, and quality testing procedures. Chinese production benefits from established supply chains for nickel processing and rare-earth element refining, though these advantages are offset by coal-dependent electricity generation in major manufacturing provinces.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 555 gCO2/kWh | 28.0 | Baseline |
| South Korea | 436 gCO2/kWh | 24.8 | -11.4% |
| Japan | 462 gCO2/kWh | 25.6 | -8.6% |
| Germany | 366 gCO2/kWh | 22.1 | -21.1% |
| France | 83 gCO2/kWh | 16.2 | -42.1% |
Provenance Override Guidance
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Manufacturing facility energy consumption data with specific electricity sources and renewable energy certificates demonstrating actual grid mix or on-site generation.
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Primary material sourcing documentation showing nickel ore origin, rare-earth element supply chains, and associated transportation distances from extraction sites.
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Battery chemistry specifications detailing exact nickel content, rare-earth element composition, and alternative materials that may reduce extraction impacts.
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End-of-life processing agreements with certified recycling facilities showing material recovery rates and avoided impacts from secondary material production.
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Production volume and capacity utilization data enabling accurate allocation of facility overhead emissions across battery manufacturing operations.
Methodology Notes
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The CCI score represents cradle-to-gate emissions for one standard AA NiMH rechargeable battery excluding use-phase electricity consumption and final disposal.
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Scope 3 dominance reflects upstream impacts from nickel mining, rare-earth element extraction, and international shipping of raw materials to manufacturing facilities.
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Functional unit assumes single battery production without accounting for superior lifecycle performance compared to disposable alternatives across multiple recharge cycles.
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Assessment excludes packaging materials, retail distribution beyond factory gate, and potential avoided emissions from reduced alkaline battery consumption.
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Data gaps include regional variation in mining practices, transportation mode assumptions, and recycling credit methodologies that may significantly affect total carbon footprint.
Related Concepts
Sources
- Hedgehog 2025 LCA Report — Comprehensive lifecycle assessment demonstrating rechargeable batteries' superior environmental performance over multiple use cycles.
- Porzio & Scown 2021 Advanced Energy Materials — Analysis showing manufacturing energy represents approximately one-third of total primary energy demand for battery technologies.
- ScienceDirect 2020 Life Cycle Analysis AA Batteries — Comparative study revealing 76% lower climate impact for NiMH batteries versus alkaline alternatives over 50 cycles.
- ANL 2010 Battery Life-Cycle Analysis Review — Technical review identifying material extraction and manufacturing as dominant carbon hotspots in battery production.
- Tenergy 2024 Rechargeable Battery Knowledge Base — Industry database documenting recharge capacity of 500-1000 cycles for modern NiMH battery chemistry.