Gym Bag (nylon)
ApparelCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 2.6 | 8% | |
| Scope 2 | 8 | 25% | |
| Scope 3 | 21.4 | 67% | |
| Total | 32 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| nylon raw material production and polymerization | S3 | 38% |
| fiber spinning and extrusion (high-temperature energy use) | S3 | 22% |
| transportation and logistics | S3 | 18% |
| dyeing and finishing processes | S3 | 16% |
| end-of-life (landfill/disposal) | S3 | 6% |
Manufacturing Geography
- Region
- China
- Grid Intensity
- 555 kgCO2e/MWh (China National Grid, 2024)
Material Composition Assumptions
A typical nylon gym bag weighs approximately 600 grams and consists primarily of polyamide fibers derived from petroleum-based chemicals and monomers. The main fabric component comprises nylon 6 or nylon 66 fibers, representing roughly 85% of the total weight at 510 grams. Additional materials include reinforcement threads or linings made from polyester, cotton, or supplementary nylon layers, accounting for the remaining 15% at 90 grams. Hardware components such as zippers, buckles, and straps contribute minimal weight but involve separate manufacturing processes with their own carbon footprints.
Manufacturing Geography
China dominates global nylon textile production due to established petrochemical infrastructure and competitive manufacturing costs. The country’s electricity grid relies heavily on coal-fired power generation, resulting in a grid intensity of 555 kgCO2e/MWh. This fossil fuel dependence significantly amplifies the carbon footprint of energy-intensive nylon production processes, including polymerization reactions that require sustained high temperatures and mechanical fiber spinning operations. Chinese factories also benefit from proximity to raw material suppliers and integrated supply chains that reduce transportation costs but concentrate emissions within regions using carbon-intensive energy sources.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 555 kgCO2e/MWh | 32.0 | Baseline |
| India | 708 kgCO2e/MWh | 36.8 | +15% |
| Turkey | 387 kgCO2e/MWh | 26.4 | -17% |
| Portugal | 252 kgCO2e/MWh | 21.1 | -34% |
| Costa Rica | 35 kgCO2e/MWh | 12.8 | -60% |
Provenance Override Guidance
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Submit primary energy consumption data from nylon polymerization and fiber spinning operations, including electricity usage per kilogram of finished fabric and fuel consumption for process heating requirements.
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Provide documentation of raw material sourcing showing the proportion of virgin versus recycled nylon content, along with supplier-specific emission factors for polyamide resin production.
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Supply regional grid intensity data or renewable energy certificates demonstrating the carbon intensity of electricity used during manufacturing operations at the specific facility.
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Document transportation distances and modes for raw materials and finished products, including shipping from chemical suppliers to textile mills and from manufacturing facilities to distribution centers.
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Share dyeing and finishing process specifications detailing chemical usage, water consumption, energy requirements, and any waste treatment or recovery systems implemented.
Methodology Notes
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The CCI score represents cradle-to-gate emissions for a standard 600-gram nylon gym bag, encompassing raw material extraction through completed manufacturing but excluding use phase and disposal impacts.
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Scope 3 emissions dominate the footprint due to upstream petroleum refining, chemical synthesis, and polymerization processes required to produce virgin nylon fibers from fossil fuel feedstocks.
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The functional unit assumes a single gym bag with typical construction methods and material weights based on market analysis of common sports equipment bags.
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Exclusions include packaging materials, retail operations, consumer use patterns, and end-of-life treatment scenarios, though the methodology acknowledges nylon’s non-biodegradable properties create long-term environmental persistence.
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Data gaps exist around region-specific manufacturing efficiency improvements, the adoption rate of recycled content in consumer bags, and variations in dyeing processes that could significantly alter emission profiles.
Related Concepts
Sources
- Arbor (2024) Carbon Footprint of Sports Equipment Bags — Study found synthetic sports bags average 28.5 kg CO2e across a range of 12-45 kg CO2e.
- Thomas et al. (2009) A Carbon Footprint for UK Clothing and Opportunities for Savings — Research identified energy-intensive manufacturing processes as primary emission drivers in synthetic textile production.
- He et al. (2024) Decarbonizing Polyamide Textile Production in China, Science Direct — Analysis revealed nylon textile production in China generates 35.37 kg CO2-eq per kg, nearly four times higher than cotton.
- Geopelie (2025) The Environmental Impact of Different Textile Fibers — Report highlighted that virgin nylon produces 6.52 kg CO2e per kg compared to only 0.201 kg CO2e per kg for recycled nylon.
- Impactful Ninja (2024) How Sustainable Are Nylon Fabrics: A Life-Cycle Analysis — Assessment documented that nylon manufacturing requires fossil fuel-intensive polymerization and high-temperature fiber spinning processes.
- Good On You (2025) Material Guide: How Sustainable is Nylon — Guide noted that nylon products persist in landfills for 30-40+ years due to non-biodegradable properties.