Laundry Detergent (1L liquid)
Home & Personal CareCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 0.76 | 2% | |
| Scope 2 | 2.66 | 7% | |
| Scope 3 | 34.58 | 91% | |
| Total | 38 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| surfactant production (fatty alcohol sulfate) | S3 | 79% |
| PET/HDPE packaging materials | S3 | 12% |
| manufacturing energy and emissions | S1/S2 | 5% |
| transportation of finished product | S3 | 3% |
| use phase water heating | S3 | 1% |
Manufacturing Geography
- Region
- China, India, United States
- Grid Intensity
- 555 gCO2/kWh (China national average, IEA 2023)
Material Composition Assumptions
A typical one-liter bottle of liquid laundry detergent weighs approximately 1,120 grams including packaging. The formulation consists of builders comprising the largest portion at 560 grams or 50% by weight, primarily zeolites, sodium silicate, sodium citrate, and sodium carbonate for water softening and soil suspension. Surfactants make up 168 grams or 15% of the product weight, predominantly linear alkylbenzene sulfonates or fatty alcohol sulfates that provide cleaning action through dirt removal and foam generation.
Bleaching agents contribute 78 grams or 7% of the total weight, typically sodium percarbonate or chlorine-based compounds for stain removal and whitening. Enzymes represent a smaller but critical component at 22 grams or 2%, including proteases for protein-based stains, lipases for grease removal, and amylases for carbohydrate-based soils. The remaining 292 grams consist of fragrances derived from synthetic petroleum compounds, preservatives, colorants, and water as a carrier medium.
The packaging consists of either polyethylene terephthalate or high-density polyethylene plastic weighing approximately 45-60 grams for the bottle and closure system.
Manufacturing Geography
Liquid laundry detergent production occurs primarily in China, India, and the United States, which collectively account for over 60% of global manufacturing capacity. China serves as the dominant manufacturing hub due to established petrochemical supply chains for surfactant production and lower labor costs, operating with a grid intensity of 555 gCO2/kWh that significantly influences the carbon footprint of energy-intensive chemical processing.
Indian facilities benefit from proximity to palm oil feedstocks used in surfactant manufacturing and growing domestic demand, though grid intensity remains relatively high. United States production focuses on domestic market supply and benefits from natural gas availability for chemical processing, though regional grid intensities vary substantially between manufacturing states.
The concentration of surfactant precursor production in Asia, particularly fatty alcohol and ethylene oxide manufacturing, drives the geographic distribution of final detergent assembly operations to minimize transportation costs of bulk chemical intermediates.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 555 gCO2/kWh | 38 | Baseline |
| India | 709 gCO2/kWh | 41 | +8% |
| United States | 386 gCO2/kWh | 35 | -8% |
| European Union | 253 gCO2/kWh | 32 | -16% |
| Brazil | 91 gCO2/kWh | 28 | -26% |
Provenance Override Guidance
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Primary surfactant supplier carbon footprint data with breakdown by surfactant type (anionic vs nonionic) and feedstock source (palm kernel vs petroleum-derived fatty alcohols).
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Packaging material specifications including recycled content percentage, material type selection between PET and HDPE options, and supplier-specific production emissions data.
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Manufacturing facility energy consumption profile including electricity grid source verification, natural gas usage for heating processes, and facility-specific efficiency metrics.
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Transportation logistics documentation covering raw material inbound shipping distances and modes, finished product distribution patterns, and packaging density optimization measures.
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Product concentration factor validation showing actual grams per wash load and number of wash cycles per bottle to confirm functional unit calculations.
Methodology Notes
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The CCI score represents cradle-to-gate emissions including raw material extraction, chemical processing, packaging production, and manufacturing through distribution center delivery, but excludes consumer use phase and end-of-life disposal.
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Scope 3 emissions dominate at 91% primarily due to energy-intensive surfactant manufacturing from petrochemical feedstocks, while direct manufacturing emissions remain relatively minor compared to upstream chemical production impacts.
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Functional unit assumes standard concentration formula providing 20 wash loads per liter bottle, with each wash using approximately 50 grams of product under typical European washing machine conditions.
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Water consumption during manufacturing and raw material production stages are excluded from carbon accounting but represent significant environmental impacts estimated at 5.4 liters per liter of finished product.
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Use phase emissions from water heating during washing cycles contribute substantially to total product lifecycle impact but fall outside the cradle-to-gate CCI scope, varying significantly by regional energy sources and consumer washing temperature preferences.
Related Concepts
Sources
- Martinez et al. 2023 Environmental Science and Pollution Research — Found carbon footprints of liquid laundry detergents range from 0.31-0.52 kg CO2 equivalent per liter depending on formulation choices.
- García-Herrador et al. 2020 MDPI Sustainability — Determined that raw material procurement contributes 91% of climate impacts, with surfactant production being the dominant factor.
- Smith School of Enterprise and Environment 2023 Oxford Report — Analyzed regional variations in detergent lifecycle impacts based on electricity grid carbon intensity differences.
- AISE 2019 Product Environmental Footprint Category Rules — Established standardized methodology for calculating environmental impacts of household cleaning products including functional unit definitions.
- Bajpai & Tyagi 2007 Journal of Oleo Science — Characterized the environmental impacts of different surfactant types used in detergent formulations.