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Life cycle assessment of the manufacture of lactide and PLA biopolymers from sugarcane in Thailand

  • Wim J. Groot
  • Tobias Borén
CARBON FOOTPRINTING

Abstract

Background

l-lactide is the monomer for the polymer poly-l-lactic acid (PLLA). PLLA can be made from renewable resources, and is used in an increasing amount of applications. The biopolymer PLLA is one type of polymer of the family of polylactic acids (PLAs). Purac produces l-lactide and d-lactide, and supports partners with know-how to produce their own PLA from lactide. This life cycle assessment (LCA) study supporting market development presents the eco-profile of lactides and PLA biopolymers.

Method

An LCA was carried out for l-lactide, d-lactide, PLLA, and two PLLA/PDLA blends made from cane sugar in Thailand, and were compared with that of fossil-based polymers. The LCA complies with ISO standards, and is a cradle-to-gate analysis including sugarcane cultivation, sugarcane milling, auxiliary chemicals production, transport, and production of lactide and PLAs. In the analysis, process data were taken from the designs of full-scale plants for the production of lactic acid, lactides, and PLA. The data were combined with ecoprofiles of chemicals and utilities and recalculated to the following environmental impacts: primary renewable and non-renewable energy, non-renewable abiotic resource usage, farm land use, global warming, acidification, photochemical ozone creation, human toxicity, and eutrophication.

Results and discussion

On a weight-by-weight basis, PLLA results in significantly lower emissions of greenhouse gasses, and less use of material resources and non-renewable energy, compared to fossil-based polymers. With the present calculations, the Global Warming Potential (GWP) in l-lactide production is 300–600 kg CO2 eq./tonne and for PLLA 500–800 kg CO2 eq./tonne. The range indicates the sensitivity of the GWP to the energy credit for electricity production from bagasse in the sugar mill. The GWP of PLLA/PDLA blends with increased heat resistance is also lower compared to fossil based polymers with similar durable character. Being based on an agricultural system the biobased PLA gives rise to higher contributions to acidification, photochemical ozone creation, eutrophication, and farm land use compared to the fossil polymers.

Conclusions

The application spectrum of PLAs is expanding, and there are opportunities to replace various fossil-based polymers. This facilitates climate change mitigation and reduces dependence on fossil and scarce resources while promoting the use of local and renewable resources. It is evident that in emerging green economies agricultural technology will form an integral part in the changeover towards a more sustainable industry and society.

Keywords

Biopolymers Lactide Life cycle assessment Polylactic acids (PLAs) Poly-l-lactic acid (PLLA) Sugarcane Sustainable development Thailand 

References

  1. Althaus H-J, Chudacoff M, Hischier R, Jungbluth N, Osses M, Primas A (2007) Life cycle inventories of chemicals. Ecoinvent report No. 8, v2.0. EMPA Dübendorf, Swiss Centre for Life Cycle InventoriesGoogle Scholar
  2. Börjesson P, Berglund M (2003) Environmental analysis of biogas systems. Report No 45. Lund University, Department of Technology and Society, Environmental and Energy Systems StudiesGoogle Scholar
  3. Brännström-Norberg B-M, Dethlefsen U, Johansson R, Setterwall C, Tunbrant S (1996) Livscykelanalys för Vattenfalls elproduktion - Sammanfattande rapport, in Swedish, Vattenfall ABGoogle Scholar
  4. Chen CPJ, Chou CC (1993) Cane sugar handbook, 12th edn. Wiley, New YorkGoogle Scholar
  5. Davis J, Haglund C (1999) Life Cycle Inventory (LCI) of fertiliser production. Fertiliser products used in Sweden and Western Europe. SIK Report No 654. The Swedish Institute For Food And BiotechnologyGoogle Scholar
  6. Dones R, Bauer C, Bolliger R, Burger B, Faist Emmenegger M, Frischknecht R, Heck T, Jungbluth N, Röder A, Tuchschmid M (2007) Life cycle inventories of energy systems: results for current systems in Switzerland and other UCTE countries. Ecoinvent report no. 5. Paul Scherrer Institut Villigen, Swiss Centre for Life Cycle Inventories, Dübendorf, CHGoogle Scholar
  7. EPA European Plastics Organization. Accessed from http://lca.plasticseurope.org/index.htm. Accessed on November 2009.
  8. EPPO (2009) Energy Policy & Planning Office Thailand. Accessed from www.eppo.go.th/power/data. Accessed on November 2009.
  9. GaBi Databases (2006) PE International GmbH, LBP University of Stuttgart: GaBi 4 LCA and DfE Software, Leinfelden-EchterdingenGoogle Scholar
  10. Garlotta D (2002) A literature review of poly(lactic) acid. J Polymer Environ 9:63–84CrossRefGoogle Scholar
  11. Guinée B et al (2002) Handbook on life cycle assessment. Operational Guide to the ISO Standards. Centre of Environmental Science, Leiden University (CML)Google Scholar
  12. Hall et al (1996) NOx emissions from soil: impkications for air quality modeling in agricultural regions. Univ. California, Department of Environmental Science, Policy, and Management, Division of Ecosystem Sciences, BerkeleyGoogle Scholar
  13. IEA International Energy Agency. Accessed from www.iea.org. Accessed on November 2009.
  14. IFEU, Institut fur Energie und Umweltforschung, Heidelberg (2006) Life cycle assessment Polylactide (PLA). Study on PLA packaging material recycling. Accessed from www.IFEU.org. Accessed 2009.
  15. IPCC (2000) Good practice guidance and uncertainty management in national greenhouse gas inventories. IPCC National Greenhouse Gas Inventory ProgramGoogle Scholar
  16. IPCC (2007) Solomon et al (eds) In: Climate change 2007: the physical science basis. Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge University PressGoogle Scholar
  17. ISO (2006a) ISO 14040: Environmental management—life cycle assessment—principals and framework. International Organization for Standardization, GenevaGoogle Scholar
  18. ISO (2006b) ISO 14044: Environmental management—life cycle assessment—requirements and guidelines. International Organization for Standardization, GenevaGoogle Scholar
  19. Kellenberger D, Althaus H-J, Jungbluth N, Künniger T, Lehmann M, Thalmann P (2007) Life cycle inventories of building products. Final report ecoinvent Data v2.0 No. 7. EMPA Dübendorf, Swiss Centre for Life Cycle InventoriesGoogle Scholar
  20. Narayan R (2004) Drivers & Rationale for Use of Biobased Materials Based on Life Cycle Assessment (LCA), GPC Paper Abstract #18Google Scholar
  21. Narayan R (2009) The value proposition for using bioplastics/products, Tutorial PIRA Workshop 8 Sept. 2009Google Scholar
  22. Nemecek T, Kägi T (2007) Life cycle inventories of Swiss and European agricultural production systems. Final report ecoinvent V2.0 No. 15a Agroscope Reckenholz-Taenikon Research Station ART, Swiss Centre for Life Cycle InventoriesGoogle Scholar
  23. Nguyen TTL (2007) Life cycle assessment of bio-ethanol as an alternative transportation fuel in Thailand. Ph.D. Thesis, King Mongkut’s University of Technology Thonburi, BangkokGoogle Scholar
  24. Ometto AR, Hauschild MZ, Roma WNL (2009) Lifecycle assessment of fuel ethanol from sugarcane in Brazil. Int J Life Cycle Assess 4:236–247CrossRefGoogle Scholar
  25. Shen L, Haufe J, Patel MK (2009) Overview and market projection of emerging bio-based plastics, Pro-Bip Final Report 2009. Accessed from www.chem.uu.nl. Accessed on November 2009.
  26. van der Poel PW, Schiweck H, Schwartz (1998) Sugar technology. Verlag Dr. Albert Bartens KG, BerlinGoogle Scholar
  27. Vattenfall (2009) Vattenfall AB GENERATION NORDIC Certified Environmental Product Declaration EPD® of electricity from Vattenfall´s Nordic Hydropower. Accessed from www.environdec.com. Accessed November 2009.
  28. Vink ETH, Rabago KR, Glassner DA, Gruber PR (2003) Applications of life cycle assessment to Nature works polylactide (PLA) production. Polym Degrad Stab 80:403–419CrossRefGoogle Scholar
  29. Vink ETH, Glassner DA, Kolstad JJ, Wooley RJ, O’Connor RP (2007) The eco-profiles for current and near-future Nature works polylactide (PLA) production. Ind Biotechnol 3:58–81CrossRefGoogle Scholar
  30. Wang M, Saricks C, Wu M (1997) Fuel cycle energy use and greenhouse gas emissions of fuel ethanol produced from Midwest corn. Center for transportation research, Argonne National LaboratoryGoogle Scholar

Copyright information

© Springer-Verlag 2010

Authors and Affiliations

  1. 1.Purac–Research and DevelopmentGorinchemThe Netherlands
  2. 2.AkzoNobel, Sustainable Development, Technology & EngineeringGothenburgSweden

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