Ceramics & Glassware
HousewaresCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-07
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 1.2 | 40% | |
| Scope 2 | 0.6 | 20% | |
| Scope 3 | 1.2 | 40% | |
| Total | 3 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| Kiln firing (natural gas or coal, 1000-1300°C) | S1 | 40% |
| Forming and drying (electricity for presses, dryers) | S2 | 20% |
| Raw material extraction and processing (clay, feldspar, silica) | S3 | 18% |
| Glaze production and application (frit melting, metal oxides) | S3 | 12% |
| Packaging and transport (weight-intensive, breakage buffer) | S3 | 10% |
Manufacturing Geography
- Region
- China, EU (Germany, UK, Portugal), Japan
- Grid Intensity
- 565 gCO2e/kWh (IEA 2024, China); 350 gCO2e/kWh (IEA 2024, Germany)
Material Composition Assumptions
The default reference product is a ceramic mug weighing approximately 0.35 kg (350 g), or equivalently a glass tumbler weighing approximately 0.3 kg (300 g). The CCI score of 3 kgCO2e applies to the ceramic mug; glass tumblers are approximately 15-20% lower.
Ceramic mug composition:
- Ceramic body: Stoneware or porcelain clay body, approximately 330 g. Composed of ball clay (25-30%), china clay/kaite (20-25%), feldspar (20-25%), and silica (20-25%) by dry weight.
- Glaze: Vitreous glaze coating, approximately 10-20 g. Composed of silica, feldspar, metal oxides (for color), and fritting agents. Applied by dipping or spraying before the glost (glaze) firing.
Glass tumbler composition:
- Soda-lime glass: Approximately 300 g. Composed of silica sand (70-75%), soda ash/sodium carbonate (12-15%), limestone (10-12%), and minor additives. Melted at 1500-1600 degC in a continuous tank furnace.
Both ceramic and glass production are dominated by high-temperature thermal processes — kiln firing for ceramics (1000-1300 degC) and furnace melting for glass (1500-1600 degC). These thermal processes are predominantly fueled by natural gas (or coal in some Chinese and Indian facilities), making Scope 1 emissions the largest single contributor.
Manufacturing Geography
Ceramics and glassware production is concentrated in specific regional clusters:
- China: World’s largest producer of both ceramics (Jingdezhen, Chaozhou, Dehua) and household glassware. Exports the majority of global tableware volume.
- EU: Germany (Villeroy & Boch), UK (Stoke-on-Trent/Potteries), Portugal, and Italy have longstanding ceramic traditions. French and German glassware production (e.g., Arc International, Schott).
- Japan: Premium ceramic production (Arita, Seto, Mino regions).
- Grid intensity (China): 565 gCO2e/kWh (IEA 2024). Used as conservative default.
- Grid intensity (Germany): 350 gCO2e/kWh (IEA 2024).
- Rationale: Kiln firing is the dominant energy input and uses direct combustion (natural gas or coal), making Scope 1 emissions relatively high (40% of total). Grid electricity is used primarily for clay preparation (milling, mixing), forming (jiggering, pressing, casting), and drying. Chinese production often uses coal-fired kilns, which have higher CO2 intensity per unit of thermal output than gas-fired kilns.
Regional Variation
| Manufacturing Region | Grid Intensity | Kiln Fuel | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|---|
| China — coal kiln (default) | ~565 gCO2e/kWh | Coal | 3.0 kgCO2e | Baseline |
| China — gas kiln | ~565 gCO2e/kWh | Natural gas | 2.5 kgCO2e | -17% |
| UK (Stoke-on-Trent) | ~210 gCO2e/kWh | Natural gas | 2.0 kgCO2e | -33% |
| Germany | ~350 gCO2e/kWh | Natural gas | 2.2 kgCO2e | -27% |
| Japan | ~460 gCO2e/kWh | Natural gas/LPG | 2.4 kgCO2e | -20% |
Note: Kiln fuel type has a larger effect on total emissions than grid intensity, because Scope 1 (direct kiln combustion) is the single largest emission source at 40% of total. Switching from coal to natural gas reduces kiln CO2 emissions by approximately 40%.
Provenance Override Guidance
A supplier or manufacturer may override the default CCI score by submitting:
- Environmental Product Declaration (EPD) or Product Carbon Footprint (PCF) per ISO 14067 covering raw materials through finished product.
- Kiln energy data: Fuel type (natural gas, LPG, coal, electric), kiln efficiency, firing temperature and cycle time. Electric kilns powered by renewable electricity can reduce Scope 1 emissions to near zero.
- Factory energy data: Renewable electricity procurement for forming and drying stages.
- Cullet/recycled content (for glassware): Recycled glass (cullet) reduces melting energy by approximately 2.5% for every 10% increase in cullet content. High-cullet glass production (70-90% recycled) can reduce production emissions by 25-40%.
- Lightweight design: Thinner walls and optimized shapes reduce material use and kiln energy per piece.
Methodology Notes
- CCI score of 3 kgCO2e represents a conservative estimate for a ceramic mug (~350 g) produced in China with coal-fired kilns. WRAP/University of Sheffield (2010) reports 2-4 kgCO2e per mug. Almeida et al. (2016) reports 2-3.5 kgCO2e/kg for ceramic tile, broadly consistent on a per-kg basis.
- Scope breakdown: Scope 1 is unusually high at 40% (1.2 kgCO2e), driven by direct combustion in kilns. Scope 2 is 20% (0.6 kgCO2e) from grid electricity for forming, drying, and finishing. Scope 3 is 40% (1.2 kgCO2e) from raw material extraction, glaze production, and transport.
- Functional unit: One ceramic mug (~350 g), cradle to gate through finished glazed product.
- Glass comparison: A comparable glass tumbler (~300 g) has approximately 2.0-2.5 kgCO2e cradle to gate, lower than ceramics primarily because glass furnaces are more thermally efficient than ceramic kilns and soda-lime glass has lower chemical process emissions.
- Data gaps: Significant variation exists between earthenware (fired at 950-1100 degC), stoneware (1200-1300 degC), and porcelain (1260-1400 degC). Higher firing temperatures increase kiln energy consumption approximately proportionally. The default score assumes stoneware-grade firing.
- Durability context: Ceramics and glass have essentially infinite material lifespans but are fragile. Breakage during transport and use is a significant contributor to lifecycle waste. Per-use emissions depend heavily on product longevity.
Related Concepts
Related Categories
Sources
- British Ceramic Confederation (2019) — UK Ceramics Sector Decarbonisation Assessment. Documents energy consumption and CO2 emissions for UK tableware and sanitaryware production. Kiln firing accounts for 60-70% of manufacturing energy.
- Almeida et al. (2016) — Life cycle assessment of a ceramic tile product. Journal of Cleaner Production, 131, 583-593. Reports cradle-to-gate emissions of approximately 2.0-3.5 kgCO2e/kg for ceramic tile, with kiln firing as the dominant emission source.
- Ros-Dosdá et al. (2018) — Environmental profile of Spanish porcelain stoneware tiles. Science of the Total Environment, 648, 1427-1438. Detailed LCA of ceramic products including raw material extraction, forming, and firing stages.
- WRAP / University of Sheffield (2010) — Environmental Assessment of Consumer Products: Tableware. Lifecycle study of ceramic mugs and plates, reporting approximately 2-4 kgCO2e per ceramic mug depending on manufacturing location and kiln type.
- IEA (2024) — Emissions Factors 2024. Grid carbon intensities for major ceramics producing countries: China 565, Germany 350, UK 210, Japan 460 gCO2e/kWh.
- Vince et al. (2008) — LCA of glass beverage containers. Waste Management, 29(8), 2485-2496. Provides comparative data for soda-lime glass production including melting furnace emissions of approximately 0.7-1.0 kgCO2e/kg.