Facial Moisturizer (50ml)

Material Composition Assumptions

The typical facial moisturizer contains a water-based emulsion system with carefully balanced active and inactive ingredients. The formulation includes water as the primary base component comprising approximately 30-35 grams or 60-70% of the total product weight. Emollient oils and humectants such as glycerin and methylparaben-free alternatives contribute roughly 8-10 grams or 15-20% of the formulation weight.

Emulsifiers derived from synthetic or natural surfactants account for 2-3 grams or approximately 4-6% of the product composition, while polymeric thickeners including xanthan gum or synthetic acrylates represent 1-2 grams or 2-4% of the total weight. Preservative systems using parabens, phenoxyethanol, or plant-based extracts typically comprise less than 1 gram or under 2% of the formulation.

The packaging consists of plastic jar components manufactured from high-density polyethylene, polypropylene, or post-consumer recycled polymer blends, with the container and lid assembly weighing approximately 15-20 grams total.

Manufacturing Geography

Primary manufacturing occurs across three major cosmetics production regions with distinct energy profiles and supply chain characteristics. China serves as a dominant manufacturing hub due to lower production costs and established petrochemical infrastructure, though the national electricity grid relies heavily on coal-fired power generation at 574 gCO2/kWh intensity.

France represents European manufacturing excellence with sophisticated cosmetics clusters around Paris and Lyon, benefiting from relatively clean nuclear and renewable energy sources. South Korea has emerged as a key production center for innovative skincare formulations, particularly in Seoul and Gyeonggi regions, with moderate grid carbon intensity due to mixed energy sources.

Manufacturing location selection typically depends on target market proximity, regulatory compliance requirements, raw material availability, and labor cost considerations rather than carbon footprint optimization.

Regional Variation

Manufacturing Region	Grid Intensity	Estimated CCI Score	Adjustment vs Default
China	574 gCO2/kWh	52	Baseline
South Korea	436 gCO2/kWh	48	-8% lower
France	52 gCO2/kWh	41	-21% lower
Germany	366 gCO2/kWh	46	-12% lower
United States	386 gCO2/kWh	47	-10% lower

Provenance Override Guidance

1. Product-specific life cycle assessment data covering raw material sourcing, manufacturing energy consumption, packaging specifications, and transportation routes with third-party verification under ISO 14067 or GHG Protocol standards.

2. Detailed ingredient sourcing documentation including supplier carbon footprint data for major components such as emollient oils, preservatives, and packaging materials with geographic origin and processing method specifications.

3. Manufacturing facility energy consumption records with renewable energy certificates, grid electricity carbon intensity factors, and process-specific energy efficiency measurements for the actual production location.

4. Transportation and logistics data including shipping distances, mode selection, packaging efficiency ratios, and distribution network carbon intensity from raw material suppliers through retail delivery.

5. Packaging material specifications with recycled content percentages, material type verification, weight measurements, and end-of-life treatment assumptions based on regional waste management systems.

Methodology Notes

• The CCI score represents cradle-to-gate emissions including raw material extraction, processing, manufacturing, and packaging but excludes consumer use phase and end-of-life treatment impacts.

• Scope 3 emissions dominate the carbon footprint due to complex global supply chains for specialty cosmetic ingredients, packaging materials, and international transportation requirements.

• The functional unit assumes a standard 50ml facial moisturizer in typical plastic jar packaging with average formulation complexity and ingredient sourcing patterns.

• Consumer use phase emissions are excluded due to negligible energy consumption during application, though water heating for face washing could represent additional downstream impacts.

• Significant data gaps exist around specialty active ingredient processing, small-scale supplier emissions, and regional variations in packaging waste treatment systems.

• Transportation distances assume global average shipping patterns but actual logistics networks may vary substantially based on brand distribution strategies and regional sourcing preferences.