Abstract
Wearable healthcare electronics are rapidly emerging as a distinct electronics sector in the digital era1,2,3,4,5,6, offering substantial economic opportunities and crucial medical benefits. However, their interactions with environmental and social systems remain poorly understood7,8,9, leaving critical sustainability challenges unaddressed. Although current efforts have focused on material-level improvements, broader system-level dynamics remain unexplored. Here we present an integrated systems engineering framework based on de novo life-cycle inventories and diffusion-linked scaling to quantify global eco-footprint hotspots and identify effective mitigation strategies. Cradle-to-grave analysis of representative wearable healthcare electronics (glucose, cardiac and blood pressure monitors and diagnostic imagers) generates full-spectrum environmental impact metrics, identifying warming impacts of 1.1–6.1 kgCO2-equivalent per device. The global device consumption is projected to increase 42-fold by 2050, approaching 2 billion units annually and generating 3.4 MtCO2-equivalent emissions alongside ecotoxicity and e-waste issues. Contrary to the conventional sustainability emphasis on plastics, this work demonstrates that recyclable or biodegradable plastics offer only marginal benefits, whereas substituting critical-metal conductors and optimizing circuit architectures can significantly reduce impacts without compromising performance. This systems engineering-based life-cycle assessment framework holds promise for establishing ecologically responsible innovation in next-generation wearable electronics.
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Data availability
The research findings presented in this study are substantiated by the data included within the main body of the article as well as its Supplementary Information. Additional LCI, circuit designs and other related modelling processes can be found in the Supplementary data, Source data and a public repository (https://osf.io/bfxck/). Source data are provided with this paper.
Code availability
Scripts utilized for integrated assessment model and global mapping analysis based on Python 3.10 are available at https://osf.io/bfxck/. Source files are also provided.
References
Shi, J. et al. Active biointegrated living electronics for managing inflammation. Science 384, 1023–1030 (2024).
Chen, C., Ding, S. & Wang, J. Digital health for aging populations. Nat. Med. 29, 1623–1630 (2023).
Wang, C. et al. Bioadhesive ultrasound for long-term continuous imaging of diverse organs. Science 377, 517–523 (2022).
Gao, W. et al. Fully integrated wearable sensor arrays for multiplexed in situ perspiration analysis. Nature 529, 509–514 (2016).
Musk, E. An integrated brain-machine interface platform with thousands of channels. J. Med. Internet Res. 21, e16194 (2019).
Chortos, A., Liu, J. & Bao, Z. Pursuing prosthetic electronic skin. Nat. Mater. 15, 937–950 (2016).
Williams, E. Environmental effects of information and communications technologies. Nature 479, 354–358 (2011).
Shi, H. H. et al. Sustainable electronic textiles towards scalable commercialization. Nat. Mater. 22, 1294–1303 (2023).
Chen, S. How much energy will AI really consume? The good, the bad and the unknown. Nature 639, 22–24 (2025).
Kim, H. J., Koo, J. H., Lee, S., Hyeon, T. & Kim, D.-H. Materials design and integration strategies for soft bioelectronics in digital healthcare. Nat. Rev. Mater. 10, 654–673 (2025).
Nikolka, M., Göke, S., Burkacky, O., Spiller, P. & Patel, M. Unlocking net-zero in semiconductor manufacturing. Nat. Rev. Electr. Eng. 1, 487–488 (2024).
McCulloch, I., Chabinyc, M., Brabec, C., Nielsen, C. B. & Watkins, S. E. Sustainability considerations for organic electronic products. Nat. Mater. 22, 1304–1310 (2023).
The Global E-Waste Monitor 2024–Electronic Waste Rising Five Times Faster than Documented e-Waste Recycling (United Nations, 2024); https://ewastemonitor.info/wp-content/uploads/2024/12/GEM_2024_EN_11_NOV-web.pdf.
Yang, Q. et al. Ecoresorbable and bioresorbable microelectromechanical systems. Nat. Electron. 5, 526–538 (2022).
Jeong, H. et al. Novel eco-friendly starch paper for use in flexible, transparent and disposable organic electronics. Adv. Funct. Mater. 28, 1704433–1704442 (2018).
Zhang, Z. et al. Recyclable vitrimer-based printed circuit boards for sustainable electronics. Nat. Sustain. 7, 616–627 (2024).
Vũ, N. Đ et al. Gallium-catalyzed recycling of silicone waste with boron trichloride to yield key chlorosilanes. Science 388, 392–400 (2025).
Park, H. et al. Organic flexible electronics with closed-loop recycling for sustainable wearable technology. Nat. Electron. 7, 39–50 (2024).
Corzo, D. et al. High-performing organic electronics using terpene green solvents from renewable feedstocks. Nat. Energy 8, 62–73 (2023).
Min, J. et al. An autonomous wearable biosensor powered by a perovskite solar cell. Nat. Electron. 6, 630–641 (2023).
Cordella, M., Alfieri, F. & Sanfelix, J. Reducing the carbon footprint of ICT products through material efficiency strategies: a life cycle analysis of smartphones. J. Ind. Ecol. 25, 448–464 (2021).
Peng, P. & Shehabi, A. Regional economic potential for recycling consumer waste electronics in the United States. Nat. Sustain. 6, 93–102 (2023).
Moni, S. M., Mahmud, R., High, K. & Carbajales-Dale, M. Life cycle assessment of emerging technologies: a review. J. Ind. Ecol. 24, 52–63 (2020).
Strazza, C. et al. Technology Readiness Level—Guidance Principles for Renewable Energy Technologies Final Report (European Commission, Directorate-General for Research and Innovation, 2017).
Huijbregts, M. A. J. et al. ReCiPe2016: a harmonised life cycle impact assessment method at midpoint and endpoint level. Int. J. Life Cycle Assess. 22, 138–147 (2017).
Dexcom G6 CGM system for personal use. Dexcom https://provider.dexcom.com/products/g6-personal-cgm (2025).
Williams, E. D., Ayres, R. U. & Heller, M. The 1.7 kilogram microchip: energy and material use in the production of semiconductor devices. Environ. Sci. Technol. 36, 5504–5510 (2002).
Yang, Y. et al. A laser-engraved wearable sensor for sensitive detection of uric acid and tyrosine in sweat. Nat. Biotechnol. 38, 217–224 (2020).
Xu, Y. et al. Pencil–paper on-skin electronics. Proc. Natl Acad. Sci. USA 117, 18292–18301 (2020).
Bonnassieux, Y. et al. The 2021 flexible and printed electronics roadmap. Flex. Print. Electron. 6, 023001 (2021).
Schaubroeck, T. et al. Attributional & consequential life cycle assessment: definitions, conceptual characteristics and modelling restriction. Sustainability 13, 7386–7433 (2021).
Norgate, T. & Haque, N. Using life cycle assessment to evaluate some environmental impacts of gold production. J. Clean. Prod. 29–30, 53–63 (2012).
Bigum, M., Damgaard, A., Scheutz, C. & Christensen, T. H. Environmental impacts and resource losses of incinerating misplaced household special wastes (WEEE, batteries, ink cartridges and cables). Resour. Conserv. Recycl. 122, 251–260 (2017).
Global smartphone market soared 7% in 2024 as vendors prepare for tricky 2025. canalys.com https://canalys.com/newsroom/worldwide-smartphone-market-2024 (2025).
Yuk, H., Lu, B. & Zhao, X. Hydrogel bioelectronics. Chem. Soc. Rev. 48, 1642–1667 (2019).
Feig, V. R., Tran, H. & Bao, Z. Biodegradable polymeric materials in degradable electronic devices. ACS Cent. Sci. 4, 337–348 (2018).
Fujisaki, Y. et al. Transparent nanopaper-based flexible organic thin-film transistor array. Adv. Funct. Mater. 24, 1657–1663 (2014).
Material property data. MatWeb https://www.matweb.com/index.aspx (2025).
Fan, Z.-J. et al. Facile synthesis of graphene nanosheets via Fe reduction of exfoliated graphite oxide. ACS Nano 5, 191–198 (2011).
Worfolk, B. J. et al. Ultrahigh electrical conductivity in solution-sheared polymeric transparent films. Proc. Natl Acad. Sci. USA 112, 14138–14143 (2015).
Someya, T., Bao, Z. & Malliaras, G. G. The rise of plastic bioelectronics. Nature 540, 379–385 (2016).
Liu, H., Liu, D., Yang, J., Gao, H. & Wu, Y. Flexible electronics based on organic semiconductors: from patterned assembly to integrated applications. Small 19, 2206938 (2023).
Chu, M. et al. Co-recycling of plastics and other waste materials. Nat. Rev. Clean Technol. 1, 320–332 (2025).
Dai, Y. et al. Soft hydrogel semiconductors with augmented biointeractive functions. Science 386, 431–439 (2024).
Piao, Z., Agyei Boakye, A. A. & Yao, Y. Environmental impacts of biodegradable microplastics. Nat. Chem. Eng. 1, 661–669 (2024).
Peng, J. et al. Surface coordination layer passivates oxidation of copper. Nature 586, 390–394 (2020).
Bell, E. L. et al. Directed evolution of an efficient and thermostable PET depolymerase. Nat. Catal. 5, 673–681 (2022).
Jiang, Y. et al. A universal interface for plug-and-play assembly of stretchable devices. Nature 614, 456–462 (2023).
Sacchi, R. et al. Prospective environmental impact assement (premise): a streamlined approach to producing databases for prospective life cycle assessment using integrated assessment models. Renew. Sustain. Energy Rev. 160, 112311 (2022).
Yoshimoto, M. & Izumi, S. Recent progress of biomedical processor SoC for wearable healthcare application: a review. IEICE Trans. Electron. 102, 245–259 (2019).
Malmodin, J. & Lundén, D. The energy and carbon footprint of the global ICT and E&M sectors. Sustainability 10, 3027–3057 (2018).
Ercan M., Malmodin J., Bergmark P., Kimfalk E., & Nilsson E. Life cycle assessment of a smartphone. In Proc. ICT for Sustainability 2016 124–133 (Atlantis Press, 2016).
Suckling, J. & Lee, J. Redefining scope: the true environmental impact of smartphones? Int. J. Life Cycle Assess. 20, 1181–1196 (2015).
Zhang, T. et al. Life cycle assessment (LCA) of circular consumer electronics based on IC recycling and emerging PCB assembly materials. Sci. Rep. 14, 29183 (2024).
Zhang, M. et al. Towards sustainable perovskite light-emitting diodes. Nat. Sustain. 8, 315–324 (2025).
Yang, C. et al. A bioinspired permeable junction approach for sustainable device microfabrication. Nat. Sustain. 7, 1190–1203 (2024).
Li, P. et al. Monolithic silicon for high spatiotemporal translational photostimulation. Nature 626, 990–998 (2024).
Malmodin J. & Lövehagen N. A methodology for simplified LCAs of electronic products. In 2024 Electronics Goes Green 2024+ (EGG) 1–12 (IEEE, 2024).
Zhang, Z. et al. DeltaLCA: comparative life-cycle assessment for electronics design. In Proc. ACM on Interactive, Mobile, Wearable and Ubiquitous Technologies, Vol. 8, 1–29 (ACM, 2024).
Teer J. & Bertolini M. Reaching Breaking Point: The Semiconductor and Critical Raw Material Ecosystem at a Time of Great Power Rivalry (The Hague Centre for Strategic Studies, 2022); https://hcss.nl/wp-content/uploads/2022/10/Reaching-breaking-point-full-HCSS-2022-revised.pdf.
Pizzol, M. et al. Normalisation and weighting in life cycle assessment: quo vadis?. Int. J. Life Cycle Assess. 22, 853–866 (2017).
Wang, B., Tian, X., Stranks, S. D. & You, F. Transitioning photovoltaics to all-perovskite tandems reduces 2050 climate change impacts of PV sector by 16%. Environ. Sci. Technol. 59, 9540–9551 (2025).
Bass, F. M. A new product growth for model consumer durables. Manag. Sci. 50, 1825–1832 (2004).
Kaminski, J. Diffusion of innovation theory: theory in nursing informatics column. Can. J. Nurs. Inform. 6, 1–6 (2011).
Norton, J. A. & Bass, F. M. A diffusion theory model of adoption and substitution for successive generations of high-technology products. Manag. Sci. 33, 1069–1086 (1987).
Sultan, F., Farley, J. U. & Lehmann, D. R. A meta-analysis of applications of diffusion models. J. Mark. Res. 27, 70–77 (1990).
Managing Complications in Pregnancy and Childbirth: A Guide for Midwives and Doctors (World Health Organization, 2003).
Zhou, B. et al. Worldwide trends in hypertension prevalence and progress in treatment and control from 1990 to 2019: a pooled analysis of 1201 population-representative studies with 104 million participants. Lancet 398, 957–980 (2021).
Cardiovascular diseases (CVDs). WHO https://www.who.int/news-room/fact-sheets/detail/cardiovascular-diseases-(cvds) (2021).
Papolos, A., Narula, J., Bavishi, C., Chaudhry, F. A. & Sengupta, P. P. U.S. hospital use of echocardiography: insights from the nationwide inpatient sample. J. Am. Coll. Cardiol. 67, 502–511 (2016).
Pawar P. Apple Watch statistics by revenue, sales, series, market share, country, users and usage. Coolest Gadgets https://www.coolest-gadgets.com/apple-watches-statistics/ (2023).
Forti, V., Baldé, K. & Kuehr, R. E-waste Statistics: Guidelines on Classifications, Reporting and Indicators (United Nations Univ., 2018).
Electrical and Electronic Equipment Placed on Market Calculation Tool Manual (UNITAR, 2023); https://academy-ce.info/wp-content/uploads/2024/02/ENG-EEE-POM-calculation-tool-manual.pdf.
Miller, T. R., Duan, H., Gregory, J., Kahhat, R. & Kirchain, R. Quantifying domestic used electronics flows using a combination of material flow methodologies: a US case study. Environ. Sci. Technol. 50, 5711–5719 (2016).
Weibull formulas. What are the basic lifetime distribution models used for non-repairable populations? NIST https://www.itl.nist.gov/div898/handbook/apr/section1/apr162.htm?utm (2025).
Ciroth, A., Muller, S., Weidema, B. & Lesage, P. Empirically based uncertainty factors for the pedigree matrix in ecoinvent. Int. J. Life Cycle Assess. 21, 1338–1348 (2016).
Uncertainties. Ecoinvent Support https://support.ecoinvent.org/uncertainties (2025).
Gong, J., Darling, S. B. & You, F. Perovskite photovoltaics: life-cycle assessment of energy and environmental impacts. Energy Environ. Sci. 8, 1953–1968 (2015).
Worrell, E. et al. Potentials and Policy Implications of Energy and Material Efficiency Improvement (United Nations, 1997).
Zio XT® long-term continuous monitoring service. iRhythm Technologies https://www.irhythmtech.com/us/en/solutions-services/irhythm-service/zio-xt (2025).
Aktiia 24/7. Blood pressure monitor. Aktiia https://aktiia.com/uk/blood-pressure-monitor (2024).
Acknowledgements
We thank Z. Cheng and X. Zhong for helpful discussions. This work made use of the Pritzker Nanofabrication Facility at the Pritzker School of Molecular Engineering at the University of Chicago. B.T. acknowledges support from the US Army Research Office (W911NF-24−1-0053) and the University of Chicago startup grant. C.Y. acknowledges the support from the Suzuki Postdoctoral Fellowship. F.Y. and B.W. were supported in part by a National Science Foundation (NSF) grant (grant EFMA-2029327), the Karin Bain & John Kukral Foundation, and the Eric and Wendy Schmidt AI in Science Postdoctoral Fellowship, a programme of Schmidt Sciences, LLC.
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B.T. and F.Y. supervised the research. C.Y. and B.T. conceived of the idea and concept. C.Y. and B.W. developed the LCIA and diffusion methodologies. C.Y. and B.W. conducted the investigation, with input from A.K. C.Y. and B.W. performed the data analysis and visualization. J.W. and C.Y. conducted the electric circuit design and analysis. C.Y. drafted the paper with contributions and revisions from all authors. All authors reviewed and approved the final version of the paper.
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Extended data figures and tables
Extended Data Fig. 1 Uncertainty analysis for nCGM in terms of configuration change.
Probability distributions from uncertainty analysis of nCGM and its subcomponents (sensor, FPCB assembly, packaging, and e-waste) across GWP, FETP, TETP, HTPc, HTPnc, SOP, FFP, and WCP, based on Monte Carlo simulations (n = 10,000).
Extended Data Fig. 2 Sensitivity analysis of nCGM under configuration variations.
Overall GWP (b, e, h) and FETP (c, f, i) variations are shown for different configurations, including seven sensor designs (a-c), six FPCB modules (d-f), and five packaging scenarios with associated e-waste treatments (g-i), evaluated at the device level. Error bars denote 95% uncertainty bounds (2.5th–97.5th percentile) derived from the Ecoinvent pedigree matrix (log-normal approximation).
Extended Data Fig. 3 Attributional system boundary and simplified consequential effects for nCGM.
The attributional system boundary covers the life cycle of wearable continuous glucose monitors, including material sourcing, manufacturing, transportation, use, and end-of-life. Beyond this scope, the consequential system boundary considers healthcare system-level responses triggered by nCGM adoption. Such effects include the expansion of digital healthcare, which may displace conventional glucose monitoring (e.g., finger-prick blood glucose meters, test strips, in-clinic tests, hospital visits), but also increase upstream demands for cloud computing, flexible PCB feedstocks, and other supply-side resources. A potential rebound effect with accelerated device replacement may offset environmental gains.
Extended Data Fig. 4 Projected e-waste generation from wearable healthcare electronics.
(a) Weibull distribution parameters for 4 wearables. (b) Cumulative distribution functions (CDF) of waste generation as a function of time since market entry (n–t). (c) Projected annual e-waste generation of the four wearables under the moderate market scenario by 2050. Colored regions representing the bounds of 95% uncertainty intervals (n = 10,000). (d) Cumulative e-waste generation from 2025 to 2050 under conservative, moderate, and aggressive scenarios. Uncertainties derive from the variation of conservative, moderate, and aggressive scenarios. Error bars: standard deviations (n = 3).
Supplementary information
Supplementary Information (download PDF )
Supplementary Notes 1–9, Figs. 1–40, Tables 1–64 and References.
Supplementary Data 1 (download XLSX )
Life-cycle inventories for four wearable healthcare electronics.
Supplementary Data 2 (download XLSX )
Market diffusion data by 2050.
Supplementary Data 3 (download ZIP )
Stagewise life-cycle inventory across raw-material extraction, manufacturing, transportation, use and EOL.
Supplementary Data 4 (download XLSX )
Market-lifespan model for e-waste prediction.
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Yang, C., Wang, B., Wan, J. et al. Quantifying the global eco-footprint of wearable healthcare electronics. Nature 649, 73–82 (2026). https://doi.org/10.1038/s41586-025-09819-w
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DOI: https://doi.org/10.1038/s41586-025-09819-w


