Table 2.
comparative assessment of Biopolymer feedstock based on sustainability and productivity and limitations
| Feedstock | Biopolymer Types | Land/Water Use | Productivity (Yield %) | CO₂ Sequestration | Energy Demand | Cost Efficiency | Key Limitations | References |
|---|---|---|---|---|---|---|---|---|
| Algal Biomass | PHA, PLA, Starch, Alginates, Cellulose | Non-arable, saline/wastewater | 10–35% DCW; up to 4 g/L/day (Chlorella, Spirulina) | High | Moderate (drying, harvesting) | Improving with biorefineries | High moisture content; scale-up challenges | Mohan et al. (2022); Vickram et al. (2023) |
| Lignocellulosic Waste | PLA, PHA (via bacterial processing) | High; forestry and crop residues | 10–40% (after pretreatment) | Low | High (due to recalcitrance) | Low but feedstock is abundant | Expensive pretreatment; lignin interference | Goswami et al. (2022) |
| Bacterial Fermentation | PHA (e.g., PHB, PHV), PLA | Indirect (sugar/starch-based feed) | Up to 90% CDW (Cupriavidus necator, Ralstonia eutropha) | Low | High (sterile conditions) | Moderate–High (depends on substrate) | Requires sugars; energy and maintenance intensive | Arora et al. (2023); Bellini et al. (2022) |
| Food Waste/Glycerol | PHA, Starch blends | Low; uses existing waste streams | 15–50% (B. megaterium, Pseudomonas putida) | Medium | Moderate | High in circular systems | Variable composition and regulatory barriers | Rivas-Castillo et al. (2024) |