12V Lead-Acid Car Battery
AutomotiveCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 2.1 | 5% | |
| Scope 2 | 6.3 | 15% | |
| Scope 3 | 33.6 | 80% | |
| Total | 42 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| lead production and smelting | S3 | 40% |
| electricity consumption in manufacturing | S3 | 25% |
| plastic and polypropylene container production | S3 | 15% |
| sulfuric acid production | S3 | 10% |
| use phase - grid electricity mix | S2 | 10% |
Manufacturing Geography
- Region
- China
- Grid Intensity
- 555 kgCO2e/MWh (IEA 2023)
Material Composition Assumptions
A typical automotive lead-acid battery weighs approximately 15 kilograms and contains the following components:
- Lead and lead alloys for grid structures and active materials: 8,500g (57%)
- Lead dioxide forming the positive electrode plates: 2,100g (14%)
- Sulfuric acid electrolyte solution: 2,250g (15%)
- Polypropylene or polyethylene battery casing: 1,200g (8%)
- Plastic or glass fiber separator materials: 450g (3%)
- Lead oxide paste for electrode preparation: 500g (3%)
The predominance of lead-based materials drives the environmental profile, while the plastic housing and acid electrolyte contribute secondary impacts during manufacturing.
Manufacturing Geography
China serves as the primary manufacturing region for automotive lead-acid batteries, accounting for the largest share of global production capacity. The country’s grid electricity intensity of 555 kgCO2e per megawatt-hour significantly influences the carbon footprint of manufacturing processes. Chinese facilities benefit from established lead smelting infrastructure and integrated supply chains, though higher grid carbon intensity compared to other regions increases overall emissions. Manufacturing in China also provides cost advantages and proximity to automotive assembly operations throughout Asia.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 555 kgCO2e/MWh | 42 | Baseline |
| United States | 386 kgCO2e/MWh | 38 | -9% |
| Germany | 366 kgCO2e/MWh | 37 | -12% |
| South Korea | 436 kgCO2e/MWh | 40 | -5% |
| India | 708 kgCO2e/MWh | 47 | +12% |
Provenance Override Guidance
Suppliers can submit the following data types to override the default CCI score:
- Facility-specific electricity consumption data with hourly or monthly grid carbon intensity factors for the manufacturing location
- Lead sourcing documentation including percentage of recycled content and smelter emission factors for primary lead production
- Sulfuric acid supplier certifications with production method details and associated carbon footprint assessments
- Transportation logistics data covering raw material shipment distances and modal split between suppliers and assembly facilities
- End-of-life recycling agreements demonstrating actual collection rates and processing efficiency in target markets
Methodology Notes
- The CCI score represents cradle-to-gate emissions including raw material extraction, processing, and manufacturing through factory completion
- Scope 3 dominance reflects the carbon-intensive nature of lead smelting operations and upstream material processing activities
- Functional unit corresponds to one standard automotive battery with twelve-volt nominal voltage and typical capacity range
- Use phase charging emissions are estimated based on average grid mix but vary significantly by regional electricity sources
- End-of-life recycling benefits are excluded from the score despite high recovery rates in developed markets
- Data gaps exist for smaller regional manufacturers and emerging battery chemistry variations within lead-acid technology
Related Concepts
Sources
- Sphera Solutions 2023 Comparative LCA of Lead and LFP Batteries for Automotive Applications — Lead-acid batteries demonstrate significantly lower manufacturing environmental burdens compared to lithium-iron phosphate alternatives.
- Sullivan & Gaines 2010 Life Cycle Assessment of Battery Technologies — Lead-acid technology shows the lowest production energy requirements and emissions on both per-kilogram and per-watt-hour bases.
- International Journal of Life Cycle Assessment 2016 Lead industry life cycle studies — Lead represents the most efficiently recycled metal among commonly used industrial materials.
- Hao et al 2022 LCA of lead-acid battery with ReCiPe methodology — Material preparation activities contribute ninety-seven percent of global warming potential during the production phase.
- Schöttl et al 2025 Full life cycle assessment of industrial lead-acid battery — Battery collection and recycling rates reach ninety-nine percent across United States and European markets.