Tennis Balls (can of 3)
Sports & RecreationCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 0.07 | 8% | |
| Scope 2 | 0.16 | 18% | |
| Scope 3 | 0.67 | 74% | |
| Total | 0.9 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| raw material production (rubber & wool) | S3 | 45% |
| international transportation & logistics | S3 | 18% |
| manufacturing & chemical processing | S3 | 15% |
| packaging (plastic can) | S3 | 12% |
| end-of-life (landfill methane emissions) | S3 | 10% |
Manufacturing Geography
- Region
- East Asia (China, Thailand, Malaysia)
- Grid Intensity
- 576 gCO2/kWh (China national average, IEA 2024)
Material Composition Assumptions
The material composition for a standard can of three tennis balls totaling approximately 90 grams is estimated as follows:
- Natural rubber core material comprises roughly 77 grams or 85 percent of total ball weight
- Wool and nylon felt covering accounts for approximately 13 grams or 15 percent of total ball weight
- Pressurized plastic or aluminum cylindrical container with hermetic sealing mechanism
- Chemical adhesives and processing solvents used during manufacturing assembly
The natural rubber serves as the primary structural component providing ball bounce characteristics, while the felt covering delivers surface texture and aerodynamic properties essential for gameplay performance.
Manufacturing Geography
Tennis ball production is heavily concentrated in East Asian countries, particularly China, Thailand, and Malaysia, which collectively account for the vast majority of global output. This manufacturing concentration reflects established rubber processing capabilities, textile production infrastructure, and cost-competitive labor markets in the region.
The carbon intensity of electricity generation in these manufacturing hubs significantly influences the overall emissions profile, with China’s grid intensity averaging 576 grams of carbon dioxide per kilowatt-hour. Energy-intensive processes including rubber vulcanization, felt production, and pressurization systems directly contribute to the manufacturing carbon footprint through this grid-connected electricity consumption.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| East Asia (China) | 576 gCO2/kWh | 62 | Baseline |
| Southeast Asia (Thailand) | 423 gCO2/kWh | 57 | -8% lower |
| Europe (Germany) | 366 gCO2/kWh | 45 | -27% lower |
| North America (USA) | 386 gCO2/kWh | 48 | -23% lower |
| India | 708 gCO2/kWh | 69 | +11% higher |
Provenance Override Guidance
Suppliers can submit the following data types to override the default CCI score with facility-specific information:
- Manufacturing facility electricity consumption data with renewable energy certificates or power purchase agreements demonstrating clean energy sourcing
- Natural rubber sourcing documentation including plantation location, processing methods, and transportation distances to manufacturing facility
- Wool felt production specifications detailing fiber origins, chemical processing inputs, and dyeing or treatment procedures
- Transportation and logistics records showing shipping routes, modal splits, and packaging efficiency metrics from raw material suppliers through final distribution
- End-of-life management programs including take-back initiatives, recycling partnerships, or alternative disposal methods that avoid conventional landfilling
Methodology Notes
- The CCI score represents cradle-to-grave emissions including raw material extraction, manufacturing, transportation, and end-of-life disposal for one pressurized can containing three tennis balls
- Scope 3 emissions dominate the footprint due to material-intensive rubber and wool production processes combined with extensive global supply chain transportation requirements
- The functional unit accounts for the complete retail package as typically purchased by consumers rather than individual ball units
- Manufacturing energy consumption estimates exclude facility overhead and focus on direct production processes including vulcanization and pressurization equipment
- Packaging emissions include both the protective cylindrical container and any secondary retail packaging materials
- Data gaps exist for specialized chemical additives used in rubber processing and felt treatment applications
Related Concepts
Sources
- Arbor 2025 arbor.eco — Provided standard tennis ball carbon footprint baseline data across multiple manufacturing scenarios.
- EcoChain 2023 Renewaball LCA — Documented emissions reductions achieved through recyclable tennis ball design alternatives.
- Gonzalez 2025 Journal of Student Research — Analyzed sustainable material alternatives including hemp and biodegradable components for tennis ball construction.
- Laykold 2025 RecycleBalls Partnership — Quantified end-of-life impacts and recycling potential for conventional tennis ball designs.
- S&P Global 2024 Tennis Ball Supply Chains — Mapped global supply chain geography showing 96 percent of tennis ball exports originating from Asian manufacturing hubs.
- Stanford 2023 Tennis Ball Recycling — Assessed long-term environmental persistence and methane emissions from landfilled tennis balls.
- Etkiyap 2023 Sustainability Challenge — Evaluated wool felt production impacts representing the majority of environmental burden in tennis ball manufacturing.