Dumbbells (pair, rubber)
Sports & FitnessCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 1.8 | 15% | |
| Scope 2 | 2.4 | 20% | |
| Scope 3 | 7.8 | 65% | |
| Total | 12 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| raw material production (virgin or synthetic rubber) | S3 | 45% |
| metal core casting (cast iron or steel) | S3 | 25% |
| rubber coating and vulcanization energy | S1/S2 | 18% |
| transportation and packaging | S3 | 12% |
Manufacturing Geography
- Region
- China
- Grid Intensity
- 555 gCO2e/kWh (IEA 2023)
Material Composition Assumptions
A typical pair of rubber dumbbells weighing approximately 15 kilograms consists primarily of cast iron or steel cores that comprise roughly 75% of the total weight at 11,250 grams. The rubber coating, which may be natural rubber, synthetic neoprene, or recycled rubber compound, accounts for approximately 20% of the weight at 3,000 grams. Chemical additives including vulcanizing agents, plasticizers, and carbon black fillers make up the remaining 5% at roughly 750 grams.
The metal core provides the primary mass and structural integrity while the rubber coating offers grip, protection, and noise reduction. The chemical additives are essential for rubber processing, enabling vulcanization that creates the durable, flexible properties required for fitness equipment applications.
Manufacturing Geography
China dominates global dumbbell manufacturing due to established supply chains for both steel production and rubber processing. The country’s grid intensity of 555 gCO2e per kilowatt-hour significantly influences the carbon footprint during energy-intensive manufacturing stages including metal casting and rubber vulcanization.
Chinese manufacturers benefit from proximity to raw material suppliers and integrated production facilities that can handle both metalworking and rubber coating processes. The concentration of fitness equipment production in industrial regions allows for economies of scale but results in higher emissions due to coal-heavy electricity generation.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 555 gCO2e/kWh | 12.0 | Baseline |
| India | 708 gCO2e/kWh | 13.8 | +15% |
| Germany | 366 gCO2e/kWh | 10.1 | -16% |
| Taiwan | 502 gCO2e/kWh | 11.4 | -5% |
| United States | 386 gCO2e/kWh | 10.3 | -14% |
Provenance Override Guidance
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Submit detailed material composition data specifying the exact type and source of rubber used, distinguishing between natural rubber, synthetic variants like neoprene or butadiene rubber, and recycled content percentages.
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Provide energy consumption data for rubber vulcanization and metal core production processes, including electricity usage per unit and any renewable energy sourcing.
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Document transportation distances and methods for raw materials including steel or iron ore sourcing and rubber material origins.
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Supply manufacturing facility location and local grid electricity carbon intensity factors used during production.
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Specify any process modifications such as alternative vulcanization methods or energy recovery systems that reduce manufacturing emissions.
Methodology Notes
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The CCI score represents cradle-to-gate emissions for a standard pair of rubber dumbbells excluding use phase and end-of-life disposal impacts.
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Scope 3 dominates at 65% due to carbon-intensive raw material production including steel manufacturing and rubber processing which generate substantial upstream emissions.
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The functional unit is defined as one pair of dumbbells with rubber coating regardless of specific weight designation.
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Transportation emissions assume standard shipping distances from Asian manufacturing centers to global distribution points.
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Data gaps exist for specific rubber formulations and additive impacts, with synthetic rubber emissions showing high variability depending on production methods and feedstock sources.
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End-of-life impacts are excluded despite rubber’s persistence in landfill environments lasting hundreds of years without biodegradation.
Related Concepts
Sources
- Patrawoot et al. 2021 SPE Polymers — Quantified carbon intensity of synthetic rubber production processes including butadiene rubber manufacturing.
- Dunuwila et al. 2018 Environmental Analysis — Analyzed environmental impacts of rubber processing and vulcanization stages in manufacturing.
- Jawjit et al. 2010 Rubber Production Study — Documented lifecycle impacts of rubber production from raw material extraction through processing.
- Scientific Reports 2022 Life Cycle Assessment and Costing — Comprehensive assessment of rubber product manufacturing including energy consumption and emissions data.