Measuring the environmental impacts of carbon fibre: life cycle assessment
Undergraduate student Phoebe Brown visited BGS to understand the life cycle of carbon fibre, from primary production to recycling.
01/09/2026 By BGS Press
Last summer, I completed a research project in partnership with BGS and the University of Warwick. Based at BGS headquarters in Keyworth, Nottinghamshire, I worked alongside the UK Critical Minerals Intelligence Centre (CMIC), gaining first-hand experience of their work and research.
My project focused on using life-cycle assessment (LCA) methods to measure the environmental impacts of a specific product. LCA is a systematic methodology to quantify and evaluate the impacts of a product, service or process throughout its life cycle, from raw material extraction to end of life. The project involved four weeks of LCA training before I conducted my own LCA on a product of my choosing, in this case the composite material carbon fibre (CF).
As a Manufacturing and Mechanical Engineering undergraduate student, I have a particular interest in carbon fibre, for which the UK market is rapidly growing (4.9per cent compound annual growth rate). With its unique strength-to-weight properties, it’s an important material for innovation in industries such as aerospace, automotives and renewable energy technologies. However, as its use expands, CF recycling becomes ever more essential.
This raises a question: for a high-polymer content material such as CF, how much more environmentally beneficial is recycling over primary production? To answer this, I set out to perform an LCA on both primary production and recycling of CF, to compare and evaluate their consequences on human and environmental health. This was done by first understanding the primary production and recycling processes and then collating the input and output data from secondary sources.
Recycling performed substantially better than primary production across the majority of impact categories, showing large reductions in:
- climate change (91.5per cent)
- ozone depletion (95.5per cent)
- acidification (91.4per cent)
- particulate matter formulation (86per cent)
- water use (88.7per cent)
- ionising radiation (99.5per cent)
- land use (95.9per cent)
- energy resources (non-renewable) (90.6per cent)
The category βmaterial resourcesβ saw a 29.7per cent gain back into the CF life cycle, due to fibre recovery, and βhuman health: carcinogenicβ performed 21.5per cent worse in recycling compared to initial production, due to the emission of benzene (a known carcinogen) during pyrolysis.

Figure 1 Impact across impact categories for primary production vs. recycled fibres: acidification (A:T), climate change (global warming potential/GWP-100), ecotoxicity (ET:FW/M/T), energy resources (fossil) (ER), eutrophication (E:FW/M), human toxicity (HT:C/NC), ionising radiation (IR), land use (LU), material resources (MR), ozone depletion (OD), particulate matter formation (PMF), photochemical oxidant formation (POF:HH/TE), and water use (WU) Β© Phoebe Brown.
The main contributors of both processes to global warming potential (GWP) through emissions were also evaluated. CF production has a GWP of 31.2 kg CO2 Eq, caused by:
- feedstock material (52.5per cent)
- electricity (42.8per cent)
- natural gas (4per cent)
The feedstock material evaluated in this assessment was polyacrylonitrile (PAN) fibre, which is the most widely used CF. More specifically, the raw material acrylonitrile was used, which contributes 31.58per cent to the total GWP of CF production.
Recycling, on the other hand, has a GWP of 2.69 kg CO2 Eq, contributed to mostly by:
- natural gas (85.7per cent)
- transport (8.6per cent)
- electricity (5.7per cent)

Figure 2 Contributors to the primary production and recycling of carbon fibres. Β© Phoebe Brown.
This comparison highlights the importance of recycling CFs for the health of both the environment and the global population. It also recognises areas with the most impact across both production and recycling, to explore potential improvements in future studies.
Potential improvements I have highlighted are:
- alternative bio-based feedstock materials (lignin)
- net zero energy use
- implementing bio-gas alternatives instead of natural gas
- re-using the byproducts of pyrolysis recycling as fuel back into the process
- implementing alternative recycling operations industrially, such as fluidised bed or chemical recycling
My time researching this topic at BGS has been incredibly rewarding. I have learned so much about the workplace, writing research papers, sustainability and more. I thoroughly enjoyed my experience at BGS headquarters; everyone was super friendly and made me feel very welcome.
Thanks go out to Narendra Singh, Gavin Mudd, Evi Petavratzi, Maria Kariuki and the whole CMIC team at BGS for making my placement so rewarding.
Author
Phoebe Brown (undergraduate student)
Friedmann, J, Fan, Z, and Tang, K. 2019. Low-carbon heat solutions for heavy industry: sources, options, and costs today. Center on Global Energy Policy. (New York, USA: Columbia University.) Available: https://www.energypolicy.columbia.edu/publications/low-carbon-heat-solutions-heavy-industry-sources-options-and-costs-today/
Kooduvalli, K, Romero, S, Ford, S, Sloan, I, Coughlin, H, Unser, J, Vaidya, U, and Ozcan, S. 2020. . SAMPE Virtual Conference Proceedings, 2020. DOI: https://doi.org/10.33599/nasampe/s.20.0371
Meng, F, Olivetti, E A, Zhao, Y, Chang, J C, Pickering, S J, and McKechnie, J. 2018. . ACS Sustainable Chemistry & Engineering, Vol. 6(8), 9854β9865. DOI: https://doi.org/10.1021/acssuschemeng.8b01026
Pender, K, Romoli, F, Martin Rodes, F A, Fuller, J, and Zeolla, M. 2025. . Journal of Cleaner Production, Vol. 486, 144525. DOI: https://doi.org/10.1016/J.JCLEPRO.2024.144525
Wang, S, Zhang, Y, Gao, H, Jin, K, Ao, C, Tian, L, He, Q, Yi, B, Ai, P, Cao, W, Pu, Y, Cheng, Y, and Li, Q. 2025. . Green Chemistry, Vol. 27(4), 1031β1043. DOI: https://doi.org/10.1039/D4GC04579C
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