Portland Cement (25kg bag)
Construction MaterialsCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-08
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 4.4 | 5% | |
| Scope 2 | 8.8 | 10% | |
| Scope 3 | 74.8 | 85% | |
| Total | 88 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| clinker calcination | S3 | 50% |
| fossil fuel combustion in kiln | S3 | 35% |
| raw material extraction and transport | S3 | 10% |
| electricity for grinding and processing | S2 | 5% |
Manufacturing Geography
- Region
- China, India, United States
- Grid Intensity
- 550 gCO2/kWh (global cement industry average)
Material Composition Assumptions
Portland cement in a 25-kilogram bag consists primarily of clinker, which comprises the vast majority of the final product by weight. The manufacturing process begins with limestone as the dominant raw material, typically representing 23 kilograms of the total mass. Gypsum serves as a setting regulator and accounts for approximately 750 grams to 1.25 kilograms of the mixture. Silica, alumina, and iron ore function as essential chemical components that enable the hydraulic properties of the final cement, contributing the remaining weight through their incorporation during clinker formation.
The production process transforms these raw materials through high-temperature calcination in rotary kilns, where limestone undergoes chemical decomposition to form calcium oxide. This transformation fundamentally alters the molecular structure while maintaining the total mass balance in the final packaged product.
Manufacturing Geography
Global cement production concentrates in regions with abundant limestone deposits and established heavy industrial infrastructure. China dominates world production capacity, followed by India and the United States, which together account for more than half of global output. These manufacturing hubs benefit from proximity to raw materials and access to the substantial energy infrastructure required for kiln operations.
The average grid intensity for cement manufacturing regions reflects a mix of coal, natural gas, and renewable sources, with developing nations typically relying more heavily on coal-fired electricity. This regional energy profile directly influences the carbon intensity of cement production through both direct fuel combustion and electricity consumption for grinding operations.
Regional Variation
| Manufacturing Region | Grid Intensity | Estimated CCI Score | Adjustment vs Default |
|---|---|---|---|
| China | 650 gCO2/kWh | 92 | +4.5% |
| India | 700 gCO2/kWh | 95 | +8.0% |
| United States | 400 gCO2/kWh | 82 | -6.8% |
| European Union | 300 gCO2/kWh | 78 | -11.4% |
| Brazil | 350 gCO2/kWh | 80 | -9.1% |
Provenance Override Guidance
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Submit kiln-specific fuel consumption data showing actual coal, natural gas, or alternative fuel usage rates per tonne of clinker produced.
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Provide electricity consumption records from grinding and processing operations, including any renewable energy procurement agreements or on-site generation.
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Document clinker-to-cement ratio for the specific production batch, as higher ratios significantly increase process emissions from calcination.
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Supply transportation distance and mode information for major raw materials, particularly limestone and gypsum sourcing locations relative to the manufacturing facility.
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Present any carbon capture utilization or alternative cement chemistry data that reduces process emissions below industry standard formulations.
Methodology Notes
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The CCI score represents cradle-to-gate emissions for one 25-kilogram bag of ordinary Portland cement delivered to a regional distribution center.
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Scope 3 emissions dominate due to process emissions from limestone calcination, which release carbon dioxide as an unavoidable chemical byproduct regardless of energy source.
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The functional unit captures standard bag packaging typical for retail and small-scale construction applications rather than bulk industrial delivery methods.
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End-of-life carbonation, where concrete slowly reabsorbs atmospheric carbon dioxide, is excluded from the current assessment boundary.
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Data gaps include regional variations in kiln efficiency, alternative fuel substitution rates, and emerging carbon capture technologies that may reduce future emission factors.
Related Concepts
Sources
- Huntzinger & Eatmon 2009 Journal of Cleaner Production — Comprehensive lifecycle assessment establishing cement's carbon intensity range of 0.8-0.9 kg CO2 per kg produced.
- International Energy Agency 2007 GHG R&D Programme — Analysis of cement industry emissions showing clinker production dominates the carbon footprint.
- IPCC 2006 Default Emission Factors — Standardized methodology for calculating process emissions from limestone calcination in cement manufacturing.
- Barcelo et al. 2014 Materials and Structures — Regional analysis demonstrating significant variation in cement carbon intensity across different production technologies.
- NRMCA 2023 Cradle-to-Gate LCA Report — Updated assessment confirming cement's contribution to approximately eight percent of global carbon dioxide emissions.