AA Battery (single-use)
ElectronicsCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 2.6 | 5% | |
| Scope 2 | 7.8 | 15% | |
| Scope 3 | 41.6 | 80% | |
| Total | 52 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| steel production and casing manufacturing | S3 | 35% |
| zinc and manganese oxide material extraction and processing | S3 | 28% |
| battery manufacturing and assembly | S3 | 20% |
| packaging materials and transportation logistics | S3 | 12% |
| end-of-life disposal and landfill impacts | S3 | 5% |
Manufacturing Geography
- Region
- China
- Grid Intensity
- 555 gCO2e/kWh (IEA 2023)
Material Composition Assumptions
Single-use AA alkaline batteries contain several key components that contribute to their carbon footprint. The steel casing represents the largest mass fraction at approximately 8 grams or 40% of total weight. The zinc anode accounts for roughly 4 grams or 20% of battery mass. Manganese dioxide serves as the cathode material comprising about 3 grams or 15% of total weight. Potassium hydroxide electrolyte makes up approximately 2 grams or 10% of the battery. Plastic wrapper materials contribute roughly 2 grams or 10% to overall mass. Internal separator materials account for the remaining 1 gram or 5% of total battery weight, bringing the complete unit to approximately 20 grams.
Manufacturing Geography
China dominates global alkaline battery production due to established manufacturing infrastructure and access to raw material supply chains. Chinese facilities typically operate with an electricity grid intensity of 555 gCO2e per kilowatt-hour, which significantly influences the carbon footprint of battery manufacturing processes. The concentration of zinc and manganese processing facilities in this region creates logistical advantages for battery manufacturers. Energy-intensive processes like steel casing production and electrochemical cell assembly benefit from economies of scale available in Chinese industrial zones.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 555 gCO2e/kWh | 52 | Baseline |
| India | 708 gCO2e/kWh | 67 | +29% |
| Germany | 366 gCO2e/kWh | 41 | -21% |
| Japan | 462 gCO2e/kWh | 46 | -12% |
| United States | 386 gCO2e/kWh | 43 | -17% |
Provenance Override Guidance
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Primary manufacturing facility location with specific electricity grid composition data and renewable energy procurement agreements that demonstrate actual grid intensity below regional averages.
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Detailed bill of materials specifying exact quantities and sources of steel, zinc, manganese dioxide, and other component materials with supplier-specific carbon intensity data for each input.
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Transportation logistics documentation covering shipping methods, distances, and modal splits from raw material extraction through final distribution to demonstrate actual transportation emissions.
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Manufacturing process energy consumption data including specific electricity and fuel usage per battery unit with documentation of any energy efficiency improvements or renewable energy utilization.
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End-of-life management programs with documented recycling rates and recovery processes that demonstrate reduced disposal impacts compared to standard landfill scenarios.
Methodology Notes
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The CCI score represents cradle-to-grave emissions for a standard AA alkaline battery including raw material extraction, manufacturing, transportation, and end-of-life disposal impacts.
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Scope 3 emissions dominate at 80% of total impact due to upstream material production, particularly steel casing and zinc processing which require energy-intensive extraction and refining operations.
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The functional unit is defined as one complete AA alkaline battery capable of delivering 1.5 volts with standard capacity ratings for consumer electronic applications.
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The assessment excludes potential recycling benefits since most batteries currently enter waste streams rather than recovery systems, reflecting actual end-of-life scenarios in most markets.
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Data gaps exist around regional variations in raw material extraction impacts and emerging recycling technologies that may improve future end-of-life performance.
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Transportation impacts assume standard distribution networks but may vary significantly based on final market destination and logistics optimization.
Related Concepts
Sources
- Hamade et al. 2020 Procedia Manufacturing — Identified alkaline batteries as having significant environmental impacts during manufacturing phase compared to disposal.
- CalRecycle 2012 Single-Use Alkaline Battery Case Study — Found that only 6% of alkaline batteries were recycled in California with majority ending up in landfills.
- ScienceDirect 2020 Life Cycle Analysis of AA Alkaline Batteries — Demonstrated that steel casing represents the largest mass fraction and major carbon footprint contributor.
- NEMA 2011 Life Cycle Impacts of Alkaline Batteries with Focus on End-of-Life — Showed that manufacturing impacts exceed recycling impacts despite energy-intensive recycling processes.
- Hedgehog Consulting 2025 AA Alkaline vs Rechargeable Battery LCA — Determined that rechargeable batteries have 76% less environmental impact than single-use alkaline alternatives.