Biodegradable & Compostable Packaging
PackagingCarbon Cost Index Score
Per kg
Methodology v1.0 · Last reviewed 2026-04-07
Scope Breakdown
| Scope | kgCO₂e | % of Total | Distribution |
|---|---|---|---|
| Scope 1 | 0.2 | 6% | |
| Scope 2 | 0.8 | 23% | |
| Scope 3 | 2.5 | 71% | |
| Total | 3.5 | 100% |
Emission Hotspots
| Emission Hotspot | Scope | Est. % of Total |
|---|---|---|
| Feedstock cultivation (corn, sugarcane) and starch/sugar extraction | S3 | 30% |
| PLA or PHA polymerization (lactic acid fermentation, ring-opening) | S3 | 25% |
| Film extrusion or thermoforming (blown film, sheet extrusion) | S2 | 20% |
| Transport and distribution | S3 | 13% |
| Printing, lamination, and converting | S2 | 12% |
Manufacturing Geography
- Region
- USA, EU (Netherlands, Germany), China, Thailand
- Grid Intensity
- 390 gCO2e/kWh (IEA 2024, USA); 565 gCO2e/kWh (IEA 2024, China)
Material Composition Assumptions
The default reference product is 1 kg of PLA-based compostable packaging film or container, representing the most commercially widespread biodegradable packaging material:
- PLA (polylactic acid) resin: Derived from corn starch (NatureWorks Ingeo, ~70% global PLA capacity) or sugarcane. Polymerization involves starch hydrolysis, glucose fermentation to lactic acid, and ring-opening polymerization of lactide. Approximately 90-95% of finished product mass.
- Additives and processing aids: Nucleating agents, plasticizers (for flexibility), anti-block agents, and colorants, approximately 2-5% by weight.
- Alternative materials in scope: The CCI score also applies approximately to:
- PBAT (polybutylene adipate terephthalate): Petrochemical-derived but compostable. ~3.0-4.0 kgCO2e/kg.
- Starch blends (Mater-Bi type): Thermoplastic starch blended with biodegradable polyesters. ~2.0-3.5 kgCO2e/kg.
- PHA (polyhydroxyalkanoates): Microbially produced biopolymer. ~2.5-5.0 kgCO2e/kg.
PLA is the highest-volume biodegradable packaging polymer, accounting for approximately 50-60% of the bioplastics market by production capacity.
Manufacturing Geography
Biodegradable packaging production is concentrated in a few regions:
- PLA resin production: NatureWorks (USA, Blair, Nebraska) produces ~150,000 tonnes/year. TotalEnergies Corbion (Thailand) is the second-largest PLA producer. Smaller producers in China and EU.
- PBAT production: BASF (Germany, ecoflex), Novamont (Italy, Mater-Bi blends), and Chinese producers.
- PHA production: Danimer Scientific (USA), Kaneka (Japan), emerging capacity in China.
- Film conversion and thermoforming: Distributed globally, near end markets.
- Grid intensity (USA): 390 gCO2e/kWh (IEA 2024). NatureWorks uses some renewable energy.
- Grid intensity (China): 565 gCO2e/kWh (IEA 2024). Growing PLA production capacity.
- Rationale: PLA polymerization is moderately energy-intensive (fermentation, distillation, ring-opening polymerization, pelletizing). NatureWorks reports significant use of renewable energy (wind power) at its Nebraska facility, which reduces production emissions.
Regional Variation
| Resin + Conversion Region | Grid Intensity | Estimated Score (per kg) | Adjustment vs Default |
|---|---|---|---|
| USA — NatureWorks (default) | ~390 gCO2e/kWh | 3.5 kgCO2e | Baseline |
| Thailand — Corbion | ~420 gCO2e/kWh | 3.0 kgCO2e | -14% (sugarcane feedstock) |
| China | ~565 gCO2e/kWh | 4.0 kgCO2e | +14% |
| EU (Netherlands, Germany) | ~300 gCO2e/kWh | 3.0 kgCO2e | -14% |
| Japan | ~460 gCO2e/kWh | 3.6 kgCO2e | +3% |
Note: Feedstock choice (corn vs. sugarcane) affects upstream agricultural emissions. Sugarcane-based PLA typically has lower feedstock emissions than corn-based PLA due to higher yields and lower fertilizer intensity.
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 14025 / ISO 14067 for the specific bioplastic product.
- Resin supplier data: NatureWorks and TotalEnergies Corbion publish PCF data for their PLA resins.
- Feedstock sourcing data: Certified sustainable corn or sugarcane (e.g., Bonsucro for sugarcane) with verified agricultural emission data.
- Conversion facility energy data: Renewable electricity procurement for film extrusion and thermoforming.
- Compostability certification: EN 13432 (EU) or ASTM D6400 (US) certification confirms industrial compostability but does not directly address production-phase emissions.
Methodology Notes
- CCI score of 3.5 kgCO2e/kg represents a conservative estimate for PLA-based compostable packaging, consistent with Vink et al. (2010) reporting ~2.0 kgCO2e/kg for PLA resin plus conversion energy. The CCI score adds a conservative margin for generic production conditions.
- Scope breakdown: Scope 3 dominates at 71% (2.5 kgCO2e/kg), driven by corn/sugarcane cultivation, starch extraction, lactic acid fermentation, and chemical inputs. Scope 2 is 23% (0.8 kgCO2e/kg) from polymerization, extrusion, and conversion electricity. Scope 1 is 6% (0.2 kgCO2e/kg).
- Confidence: Low because the bioplastics category encompasses chemically diverse materials (PLA, PHA, PBAT, starch blends) with significantly different production processes and emission profiles. The score represents PLA as the dominant material.
- Functional unit: 1 kg of PLA-based compostable packaging film or container, cradle to gate.
- Biogenic carbon: PLA contains biogenic carbon from photosynthesis (~1.8 kgCO2e of biogenic carbon per kg of PLA). Following standard LCA conventions, biogenic carbon uptake is reported separately and excluded from the fossil GWP score.
- End-of-life caveat: Compostable packaging requires industrial composting (58 degC+ for PLA) to biodegrade. In landfill conditions, PLA degrades very slowly. The environmental benefit of compostability is only realized with proper waste infrastructure, which is not widely available.
- Comparison: PLA packaging (~3.5 kgCO2e/kg) is comparable to conventional polyethylene (~1.8-2.0 kgCO2e/kg) and polypropylene (~1.5-1.8 kgCO2e/kg) on a cradle-to-gate basis. The production-phase carbon footprint of bioplastics is generally similar to or slightly higher than conventional plastics.
Related Concepts
Related Categories
Sources
- Vink et al. (2010) — The eco-profile for current Ingeo polylactide production. Industrial Biotechnology, 6(4), 212-224. NatureWorks reports cradle-to-gate GWP of approximately 1.8-2.0 kgCO2e/kg for PLA resin (Ingeo), including corn cultivation and fermentation.
- Groot & Borén (2010) — Life cycle assessment of the manufacture of lactide and PLA biopolymers from sugarcane in Thailand. International Journal of Life Cycle Assessment, 15(9), 970-984. Reports PLA production from sugarcane at approximately 0.5-1.5 kgCO2e/kg depending on energy source.
- European Bioplastics (2022) — Environmental communications guide for bioplastics. Documents lifecycle data and environmental claims standards for PLA, PHA, starch blends, and PBAT compostable packaging materials.
- Yates & Barlow (2013) — Life cycle assessments of biodegradable, commercial biopolymers — A critical review. Resources, Conservation and Recycling, 78, 54-66. Meta-analysis reporting cradle-to-gate GWP for PLA (1.8-3.0 kgCO2e/kg), PHA (2.0-5.0 kgCO2e/kg), and starch blends (1.5-3.5 kgCO2e/kg).
- GHG Protocol (2014) — Scope 3 Calculation Guidance. Generic emission factors for bioplastic materials when supplier-specific data is unavailable.