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    bio based polymers – evolution of worldwide production capacities from 2018 to 2029 (png) (copy)

    Biomass Utilisation Worldwide 2024 (PNG)

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    Global Production Capacities of Bio-based Polymers per region 2024 (PNG)

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    Pathways to bio-based polymers (PNG)

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    Plastics Production From 1950 to 2023 (PNG)

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    Polymers and Bio-Based Shares Worldwide (2020–2025) (PNG)

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    Schematic Differentiation of Pathways of Drop-in (PNG)

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    Shares of the Produced Bio-based Polymers in Different Market Segments in 2024 (PNG)

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    bio based building blocks and polymers – global capacities, production and trends 2024–2029 (pdf)

    Bio-based Building Blocks and Polymers – Global Capacities, Production and Trends 2024–2029 (PDF)

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    2024 was a respectable year for bio-based polymers, with an overall expected CAGR of 13 % to 2029. Overall, bio-based biodegradable polymers have large installed capacities with an expected CAGR of 17 % to 2029, but the current average capacity utilisation is moderate at 65 %. In contrast, bio-based non-biodegradable polymers have a much higher utilisation rate of 90 %, but will only grow by 10 % to 2029.

    Epoxy resin and PUR production is growing moderately at 9 and 8 %, respectively, while PP and cyclic APC capacities are increasing by 30 %. Despite a decline in production of biodegradables, especially for PLA in Asia, capacities have increased by 40 %. The same applies to PHA capacities. Commercial newcomers such as casein polymers and PEF recorded a rise in production capacity and are expected to continue to grow significantly until 2029.

    DOI No.: https://doi.org/10.52548/UMTR4695

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    Bio-based Building Blocks and Polymers Global Capacities, Production and Trends 2024–2029 – Short Version (PDF)

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    2024 was a respectable year for bio-based polymers, with an overall expected CAGR of 13 % to 2029. Overall, bio-based biodegradable polymers have large installed capacities with an expected CAGR of 17 % to 2029, but the current average capacity utilisation is moderate at 65 %. In contrast, bio-based non-biodegradable polymers have a much higher utilisation rate of 90 %, but will only grow by 10 % to 2029.

    Epoxy resin and PUR production is growing moderately at 9 and 8 %, respectively, while PP and cyclic APC capacities are increasing by 30 %. Despite a decline in production of biodegradables, especially for PLA in Asia, capacities have increased by 40 %. The same applies to PHA capacities. Commercial newcomers such as casein polymers and PEF recorded a rise in production capacity and are expected to continue to grow significantly until 2029.

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    Bio-based Non Biodegradable Polymers Evolution of Worldwide Prod Capacities 2029 (PNG)

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    bio based biodegradable polymers evolution of worldwide production capacities 2029 (png)

    Bio-based Biodegradable Polymers Evolution of Worldwide Production Capacities 2029 (PNG)

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    Bio-based polymers – Evolution of worldwide production capacities from 2018 to 2029 (PNG)

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    evaluating lca approaches and methodologies for renewable carbon sources report 1 of 3 – renewable carbon in lca guidelines (march 2025) (pdf)

    Evaluating LCA Approaches and Methodologies for Renewable Carbon Sources Report 1 of 3 – Renewable Carbon in LCA Guidelines (March 2025) (PDF)

    Markets & Economy, Policy, Sustainability & Health

    145 Pages
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    Renewable Carbon in LCA Guidelines (146 pages) evaluates methodological choices which impact LCAs for products containing renewable carbon in existing LCA frameworks and guidelines. The study specifically examines the similarities and differences in the methodological choices of guidelines, as well as the implications of these methodological aspects on the resulting LCA outcomes.The frameworks were selected based on their relevance and legitimacy in the industry, academia and policy field, and include: ISO 14040/44, ISO 14067, GHG Protocol Product Standard, PACT’s Pathfinder Framework, the PCF Guideline for the chemical industry by Together for Sustainability (TfS), EPD for the construction industry – ISO 14025 and EN 15804, the Renewable Energy Directive, the Product Environmental Footprint (PEF) and the JRC’s plastics LCA methodology. One field with a particularly large methodological freedom is recycling.

    This report is the first report of a larger RCI project on LCA methodology, which includes two additional publications:

    Report 2 of 3 – Renewable Carbon in Recycling Situations
    Report 3 of 3 – Non-technical Summary

    Please find these additional reports by following the respective links at the bottom of this page.

     

    DOI No.: https://doi.org/10.52548/VCYM7822

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    evaluating lca approaches and methodologies for renewable carbon sources report 2 of 3 – renewable carbon in recycling situations (march 2025) (pdf)

    Evaluating LCA Approaches and Methodologies for Renewable Carbon Sources Report 2 of 3 – Renewable Carbon in Recycling Situations (March 2025) (PDF)

    Markets & Economy, Policy, Sustainability & Health

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    This report focuses on renewable carbon in recycling scenarios and the key challenges in LCA and carbon footprint assessments. It examines system boundaries, allocation methods, and biogenic carbon accounting approaches, highlighting their influence on sustainability evaluations. The report emphasises the cut-off and avoided-burden approaches for recycling while recommending the -1/+1 method for biogenic carbon transparency. However, it also identifies contradictions between LCA results and broader sustainability goals, such as the EU waste hierarchy, which prioritises recycling. To address these inconsistencies, the report suggests integrating LCA with additional sustainability metrics like land use and recyclability. Ultimately, refining these methodologies will enhance the accuracy and reliability of environmental assessments for bio-based and recycled materials.

    This report is the second report of a larger RCI project on LCA methodology, which includes two additional publications:

    Report 1 of 3 – Renewable Carbon in LCA Guidelines
    Report 3 of 3 – Non-technical Summary

    Please find these additional reports by following the respective links at the bottom of this page.

     

    DOI No.: https://doi.org/10.52548/QTVU8642

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    evaluating lca approaches and methodologies for renewable carbon sources report 3 of 3 – non technical summary (march 2025)

    Evaluating LCA Approaches and Methodologies for Renewable Carbon Sources Report 3 of 3 – Non-technical Summary (March 2025) (PDF)

    Markets & Economy, Policy, Sustainability & Health

    15 Pages
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    This Non-technical Summary (15 pages),highlights main insights into the project results and states key take-aways for policy-makers.

    It compares several frameworks, such as ISO 14040, Product Environmental Footprint (PEF), and GHG Protocol, finding both commonalities and critical differences in areas like biogenic carbon accounting and recycling assessment. The study identifies significant methodological flexibility in existing frameworks, leading to inconsistencies in LCA results and challenges in standardisation. Key issues include differing treatment of carbon capture and utilisation (CCU), direct air capture (DAC), and allocation of environmental burdens in multifunctional processes. Policy recommendations emphasise the need for harmonisation, improved biogenic carbon accounting, and clear guidance on emerging technologies like DAC and mass balance attribution. Overall, the study calls for refining LCA methodologies to ensure fair comparison between renewable and fossil-based carbon solutions.

    This report is the third report of a larger RCI project on LCA methodology, which includes two additional publications:

    Report 1 of 3 – Renewable Carbon in LCA Guidelines
    Report 2 of 3 – Renewable Carbon in Recycling Situations

    Please find these additional reports by following the respective links at the bottom of this page.

    DOI No.: https://doi.org/10.52548/ZEKY1803

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    suited approach: sustainable integrated technology development (png)

    SUITED approach: SUstainable Integrated TEchnology Development (PNG)

    Markets & Economy, Sustainability & Health

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    Start the ecological and economic evaluation of your technology as early as possible:

    • Continuous optimization process
    • Sustainability integrated technology development
    • SUITED as a tool for technology improvement
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    textile waste generation collection and treatment in europe 2020 (png)

    Textile-Waste-Generation-Collection-and-Treatment-in-Europe-2020 (PNG)

    Markets & Economy, Sustainability & Health

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    Bio-based-Polymer-Production-and-Bio-based-shares-2024 (PNG)

    Markets & Economy, Policy, Sustainability & Health

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    Global-Production-Capacities-of-Bio-based-Polymers-per-Region-2024

    Global-Production-Capacities-of-Bio-based-Polymers-per-Region-2024 (PNG)

    Markets & Economy, Policy, Sustainability & Health

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    bio based polymers worldwide (pdf)

    Bio-based Polymers Worldwide (PDF)

    Markets & Economy, Policy, Sustainability & Health

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    Expert insight into capacity developments, investments and new policy frameworks:
    • Firstly, global capacity for bio-based polymers will grow strongly over the next five years, much faster than for fossil-based polymers
    • Secondly, investments in new capacity will take place in China, Europe, the Middle East, and the US
    • Thirdly, investment in bio-based polymer capacities is mainly driven by policy frameworks that create demand.

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