Conditioner (250ml plastic bottle)
Personal CareCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 3.84 | 8% | |
| Scope 2 | 5.76 | 12% | |
| Scope 3 | 38.4 | 80% | |
| Total | 48 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| use phase water heating | S3 | 56% |
| raw material extraction and processing | S3 | 18% |
| packaging production (PET plastic) | S1 | 14% |
| manufacturing and product distribution | S1 | 8% |
| end-of-life disposal/recycling | S3 | 4% |
Manufacturing Geography
- Region
- China, India, Southeast Asia
- Grid Intensity
- 620 gCO2e/kWh (China National Grid 2024)
Material Composition Assumptions
A typical 250ml hair conditioner contains approximately 230g of liquid formulation and 20g of PET plastic packaging. The liquid formulation consists of conditioning agents including cetyl stearyl alcohol, lanolin, silicones, and waxes representing roughly 15% by weight. Surfactants and detergents comprise another 10% of the formulation mass. Preservatives, stabilizers, and fragrance compounds account for approximately 5% of total weight, with many fragrance compounds derived from petroleum feedstocks. The remaining 70% consists of water and minor additives that provide texture, color, and specific performance characteristics.
Manufacturing Geography
Personal care products are predominantly manufactured in China, India, and Southeast Asia due to established chemical processing infrastructure and proximity to raw material suppliers. China serves as the primary production hub with an average grid intensity of 620 gCO2e/kWh, reflecting the country’s coal-heavy electricity generation mix. Manufacturing facilities in these regions benefit from integrated supply chains for both petrochemical-derived ingredients and plastic packaging production. The concentration of PET resin production facilities in East Asia further supports regional manufacturing efficiency for bottled personal care products.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 620 gCO2e/kWh | 48 | Baseline |
| India | 650 gCO2e/kWh | 50 | +4% |
| European Union | 280 gCO2e/kWh | 38 | -21% |
| United States | 420 gCO2e/kWh | 43 | -10% |
| Brazil | 100 gCO2e/kWh | 32 | -33% |
Provenance Override Guidance
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Manufacturing facility energy consumption data with specific electricity source documentation, including renewable energy certificates or on-site generation capacity.
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Detailed ingredient sourcing information specifying the geographic origin and production methods for conditioning agents, surfactants, and fragrance compounds.
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Packaging material specifications including PET resin virgin versus recycled content percentages and bottle weight measurements.
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Transportation logistics data covering distances and modes for raw material delivery, finished product distribution, and packaging component sourcing.
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End-of-life management documentation demonstrating participation in extended producer responsibility programs or take-back systems for packaging materials.
Methodology Notes
- The CCI score represents cradle-to-grave emissions including manufacturing, distribution, consumer use phase, and end-of-life treatment for one 250ml conditioner bottle.
- Scope 3 dominance reflects significant use phase emissions from hot water heating during typical shower applications, consistent with personal care product emission patterns.
- Functional unit assumes average consumer usage patterns with warm water rinsing equivalent to standard hair washing frequency.
- Excludes indirect land use change impacts from plant-based ingredient sourcing and potential microplastic emissions during product use.
- Data gaps exist for emerging bio-based conditioning agents and regional variations in consumer behavior affecting use phase emissions.
Related Concepts
Sources
- Benavides et al. 2018 ACS Sustainable Chemistry & Engineering — Quantified PET plastic bottle production emissions ranging from 2.19-2.733 kg CO2-eq per kg of resin material.
- Trayak LLC 2021 IBWA Life Cycle Assessment — Established water heating as the dominant emission source in beverage container life cycles, applicable to personal care products.
- Cosmetics Europe & Quantis 2023 Shampoo LCA — Demonstrated that use phase emissions constitute approximately 93% of total environmental impact for hair care products.
- Andersson et al. 2021 Sustainability - Plant-Based Shampoo LCA — Analyzed raw material contributions showing roughly 25% of total environmental impact from ingredient extraction and processing.
- Baden & Quantis 2023 Carbon Trust Beauty & Personal Care Study — Found packaging represents 22% of environmental footprint for typical personal care products in plastic containers.
- EcoBeautyScore Association 2025 — Documented 20-25% emission reductions achievable through refill and refillable packaging models versus single-use bottles.
- Meta-Analysis PET Bottles 2024 Sustainability Journal — Confirmed deposit-based recycling systems significantly reduce cumulative cradle-to-grave emissions for plastic packaging.