Drain Cleaner (500ml)
HouseholdCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 2.4 | 5% | |
| Scope 2 | 7.2 | 15% | |
| Scope 3 | 38.4 | 80% | |
| Total | 48 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| plastic packaging | S3 | 35% |
| transportation to retailer | S3 | 30% |
| chemical ingredients (acids, surfactants) | S3 | 25% |
| manufacturing (electricity, gas) | S1/S2 | 10% |
Manufacturing Geography
- Region
- Western Europe
- Grid Intensity
- 295 gCO2e/kWh (EU average, 2023)
Material Composition Assumptions
A typical 500ml drain cleaner consists primarily of an aqueous solution comprising 65-85% of the total weight at approximately 325g. The active ingredients include either hydrochloric acid for heavy-duty formulations or citric and acetic acids for gentler variants, totaling roughly 15-25g. Surfactants and detergent compounds make up another 10-20g to enhance cleaning effectiveness and help break down organic blockages.
The polyethylene plastic bottle with trigger spray mechanism contributes approximately 35-45g to the total product weight. Optional fragrance compounds may add an additional 2-5g depending on the formulation. The complete packaged product typically weighs between 500-520g, with the liquid contents representing roughly 90% of the total mass.
Manufacturing Geography
Drain cleaners are predominantly manufactured in Western Europe and North America, where established chemical processing infrastructure and regulatory frameworks support household cleaning product production. The European manufacturing grid operates at an average intensity of 295 gCO2e/kWh, reflecting the region’s ongoing transition toward renewable energy sources.
Chemical synthesis facilities in these regions benefit from proximity to petrochemical feedstock suppliers and established distribution networks to major retail markets. The concentration of manufacturing in these areas also ensures compliance with stringent environmental and safety regulations governing household chemical products.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| Western Europe | 295 gCO2e/kWh | 48 | Baseline |
| North America | 386 gCO2e/kWh | 52 | +8% |
| East Asia (China) | 555 gCO2e/kWh | 63 | +31% |
| India | 708 gCO2e/kWh | 68 | +42% |
| Australia | 634 gCO2e/kWh | 61 | +27% |
Provenance Override Guidance
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Manufacturing facility energy consumption data with renewable energy procurement certificates or power purchase agreements that demonstrate below-grid-average carbon intensity.
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Transportation logistics documentation showing shipping distances and modal choices from chemical ingredient suppliers to manufacturing facilities and from facilities to distribution centers.
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Plastic packaging specifications including recycled content percentages, bottle weight optimization data, and end-of-life recyclability certifications.
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Chemical ingredient sourcing documentation detailing the production methods for acids and surfactants, including any bio-based or lower-carbon alternatives used in the formulation.
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Production efficiency metrics demonstrating manufacturing yield rates, waste reduction initiatives, and energy optimization measures that reduce per-unit environmental impact.
Methodology Notes
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The CCI score represents cradle-to-grave emissions for a complete 500ml packaged drain cleaner, including all materials, manufacturing, distribution, and end-of-life disposal impacts.
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Scope 3 emissions dominate the footprint due to upstream impacts from plastic packaging production, chemical ingredient synthesis, and transportation logistics throughout the supply chain.
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The functional unit accounts for the complete consumer-ready product including both the chemical formulation and packaging system required for safe storage and application.
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Consumer use phase emissions are excluded as they primarily involve physical application without additional energy consumption or direct emissions during the drain cleaning process.
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Data limitations exist around specific formulation variations and ingredient supplier practices, requiring estimation based on industry-average chemical production methods.
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End-of-life treatment scenarios assume typical municipal waste management practices but may not capture regional variations in plastic recycling infrastructure or hazardous waste handling protocols.
Related Concepts
Sources
- Golsteijn et al. 2016 Environmental Sciences Europe — Identified plastic packaging and ingredient sourcing as primary environmental hotspots for household cleaners.
- Nissen & Séjourné 2021 ScienceDirect — Found cradle-to-grave carbon footprint for packaged detergents averages 0.76 kg CO2-eq per kg of product.
- A.I.S.E. Charter Advanced Sustainability Profiles — Documented transportation and manufacturing impacts across the cleaning products lifecycle.