Abstract
The recent discovery of IsPETase, a hydrolytic enzyme that can deconstruct poly(ethylene terephthalate) (PET), has sparked great interest in biocatalytic approaches to recycle plastics. Realization of commercial use will require the development of robust engineered enzymes that meet the demands of industrial processes. Although rationally engineered PETases have been described, enzymes that have been experimentally optimized via directed evolution have not previously been reported. Here, we describe an automated, high-throughput directed evolution platform for engineering polymer degrading enzymes. Applying catalytic activity at elevated temperatures as a primary selection pressure, a thermostable IsPETase variant (HotPETase, Tm = 82.5 °C) was engineered that can operate at the glass transition temperature of PET. HotPETase can depolymerize semicrystalline PET more rapidly than previously reported PETases and can selectively deconstruct the PET component of a laminated multimaterial. Structural analysis of HotPETase reveals interesting features that have emerged to improve thermotolerance and catalytic performance. Our study establishes laboratory evolution as a platform for engineering useful plastic degrading enzymes.

This is a preview of subscription content, access via your institution
Relevant articles
Open Access articles citing this article.
-
Discovery and mechanism-guided engineering of BHET hydrolases for improved PET recycling and upcycling
Nature Communications Open Access 13 July 2023
-
Functional tailoring of a PET hydrolytic enzyme expressed in Pichia pastoris
Bioresources and Bioprocessing Open Access 06 April 2023
-
Investigating the effects of cyclic topology on the performance of a plastic degrading enzyme for polyethylene terephthalate degradation
Scientific Reports Open Access 23 January 2023
Access options
Access Nature and 54 other Nature Portfolio journals
Get Nature+, our best-value online-access subscription
$29.99 / 30 days
cancel any time
Subscribe to this journal
Receive 12 digital issues and online access to articles
$119.00 per year
only $9.92 per issue
Rent or buy this article
Prices vary by article type
from$1.95
to$39.95
Prices may be subject to local taxes which are calculated during checkout




Data availability
Coordinates and structure factors have been deposited in the PDB under accession number 7QVH. Data supporting the findings of this study are available within the paper and its Supplementary Information, or are available from the authors upon reasonable request.
References
Geyer, R., Jambeck, J. & Law, K. Production, use, and fate of all plastics ever made. Sci. Adv. 3, e1700782 (2017).
Jambeck, J. R. et al. Plastic waste inputs from land into the ocean. Science 347, 768–771 (2015).
Laville, S. & Taylor, M. A million bottles a minute: world’s plastic binge ‘as dangerous as climate change’. The Guardian (28 June 2017).
The New Plastics Economy: Rethinking the Future of Plastics & Catalysing Action (Ellen MacArthur Foundation, 2017); https://www.ellenmacarthurfoundation.org/publications/the-new-plastics-economy-rethinking-the-future-of-plastics-catalysing-action
Burgess, M., Holmes, H., Sharmina, M. & Shaver, M. P. The future of UK plastics recycling: one bin to rule them all. Resour. Conserv. Recycl. 164, 105191 (2021).
Rahimi, A. & García, J. M. Chemical recycling of waste plastics for new materials production. Nat. Rev. Chem. 1, 0046 (2017).
Ellis, L. D. et al. Chemical and biological catalysis for plastics recycling and upcycling. Nat. Catal. 4, 539–556 (2021).
Singh, A. et al. Techno-economic, life-cycle, and socioeconomic impact analysis of enzymatic recycling of poly(ethylene terephthalate). Joule 5, 2479–2503 (2021).
Jehanno, C. et al. Organocatalysed depolymerisation of PET in a fully sustainable cycle using thermally stable protic ionic salt. Green. Chem. 20, 1205–1212 (2018).
Karayannidis, G., Chatziavgoustis, A. P. & Achilias, D. Poly(ethylene terephthalate) recycling and recovery of pure terephthalic acid by alkaline hydrolysis. Adv. Polym. Technol. 21, 250–259 (2002).
Andrady, A. L. Assessment of environmental biodegradation of synthetic polymers. J. Macromol. Sci. C. 34, 25–76 (1994).
Herrero Acero, E. et al. Enzymatic surface hydrolysis of PET: effect of structural diversity on kinetic properties of cutinases from Thermobifida. Macromolecules 44, 4632–4640 (2011).
Sulaiman, S. et al. Isolation of a novel cutinase homolog with polyethylene terephthalate-degrading activity from leaf-branch compost by using a metagenomic approach. Appl. Environ. Microbiol. 78, 1556–1562 (2012).
Kawai, F. et al. A novel Ca2+-activated, thermostabilized polyesterase capable of hydrolyzing polyethylene terephthalate from Saccharomonospora viridis AHK190. Appl. Microbiol. Biotechnol. 98, 10053–10064 (2014).
Ribitsch, D. et al. Hydrolysis of polyethylene terephthalate by p-nitrobenzylesterase from Bacillus subtilis. Biotechnol. Prog. 27, 951–960 (2011).
Tournier, V. et al. An engineered PET depolymerase to break down and recycle plastic bottles. Nature 580, 216–219 (2020).
Zimmermann, W. Biocatalytic recycling of polyethylene terephthalate plastic. Philos. Trans. R. Soc. A. 378, 20190273 (2020).
Yoshida, S. et al. A bacterium that degrades and assimilates poly(ethylene terephthalate). Science 351, 1196–1199 (2016).
Austin, H. P. et al. Characterization and engineering of a plastic-degrading aromatic polyesterase. Proc. Natl Acad. Sci. USA 115, E4350–E4357 (2018).
Han, X. et al. Structural insight into catalytic mechanism of PET hydrolase. Nat. Commun. 8, 2106 (2017).
Joo, S. et al. Structural insight into molecular mechanism of poly(ethylene terephthalate) degradation. Nat. Commun. 9, 382 (2018).
Ronkvist, Å. M., Xie, W., Lu, W. & Gross, R. A. Cutinase-catalyzed hydrolysis of poly(ethylene terephthalate). Macromolecules 42, 5128–5138 (2009).
Wei, R. & Zimmermann, W. Biocatalysis as a green route for recycling the recalcitrant plastic polyethylene terephthalate. Microb. Biotechnol. 10, 1302–1307 (2017).
Son, H. F. et al. Rational protein engineering of thermo-stable PETase from Ideonella sakaiensis for highly efficient PET degradation. ACS Catal. 9, 3519–3526 (2019).
Son, H. F. et al. Structural bioinformatics-based protein engineering of thermo-stable PETase from Ideonella sakaiensis. Enzym. Microb. Technol. 141, 109656 (2020).
Cui, Y. et al. Computational redesign of a PETase for plastic biodegradation under ambient condition by the GRAPE strategy. ACS Catal. 11, 1340–1350 (2021).
Ma, Y. et al. Enhanced poly(ethylene terephthalate) hydrolase activity by protein engineering. Engineering 4, 888–893 (2018).
Arnold, F. H. Directed evolution: bringing new chemistry to life. Angew. Chem. Int. Ed. 57, 4143–4148 (2018).
Zeymer, C. & Hilvert, D. Directed evolution of protein catalysts. Annu. Rev. Biochem. 87, 131–157 (2018).
Zhu, B., Wang, D. & Wei, N. Enzyme discovery and engineering for sustainable plastic recycling. Trends Biotechnol. 40, 22–37 (2021).
Zhong-Johnson, E., Voigt, C. & Sinskey, A. An absorbance method for analysis of enzymatic degradation kinetics of poly(ethylene terephthalate) films. Sci. Rep. 11, 928 (2021).
Then, J. et al. A disulfide bridge in the calcium binding site of a polyester hydrolase increases its thermal stability and activity against polyethylene terephthalate. FEBS Open Bio. 6, 425–432 (2016).
Ügdüler, S. et al. Towards closed-loop recycling of multilayer and coloured PET plastic waste by alkaline hydrolysis. Green. Chem. 22, 5376–5394 (2020).
Erickson, E. et al. Comparative performance of PETase as a function of reaction conditions, substrate properties, and product accumulation. Chem. Sus. Chem. 15, e202101932 (2022).
Chen, C.-C. et al. General features to enhance enzymatic activity of poly(ethylene terephthalate) hydrolysis. Nat. Catal. 4, 425–430 (2021).
Huang, P.-S., Boyken, S. E. & Baker, D. The coming of age of de novo protein design. Nature 537, 320–327 (2016).
Dai, L. et al. Enhancing PET hydrolytic enzyme activity by fusion of the cellulose–binding domain of cellobiohydrolase I from Trichoderma reesei. J. Biotechnol. 334, 47–50 (2021).
Knott, B. C. et al. Characterization and engineering of a two-enzyme system for plastics depolymerization. Proc. Natl Acad. Sci. USA 117, 25476–25485 (2020).
Sadler, J. C. & Wallace, S. Microbial synthesis of vanillin from waste poly(ethylene terephthalate). Green. Chem. 23, 4665–4672 (2021).
Rorrer, N. A. et al. Combining reclaimed PET with bio-based monomers enables plastics upcycling. Joule 3, 1006–1027 (2019).
Anderson, J. C. et al. BglBricks: a flexible standard for biological part assembly. J. Biol. Eng. 4, 1 (2010).
Goldenzweig, A. et al. Automated structure-and sequence-based design of proteins for high bacterial expression and stability molecular cell technology automated structure-and sequence-based design of proteins for high bacterial expression and stability. Mol. Cell 63, 337–346 (2016).
Reetz, M. T. & Carballeira, J. D. Iterative saturation mutagenesis (ISM) for rapid directed evolution of functional enzymes. Nat. Protoc. 2, 891–903 (2007).
Acknowledgements
We acknowledge generous support from the Biotechnology and Biological Sciences Research Council (David Phillips Fellowship grant no. BB/M027023/1 to A.P.G), the European Research Council (ERC Starter grant no. 757991 to A.P.G), the Medical Research Council and Buddi (MRC iCASE PhD funding to E.L.B), the UK Catalysis Hub (funded through grant nos. EP/R026815/1, EP/K014706/2, EP/K014668/1, EP/K014854/1, EP/K014714/1 and EP/M013219/1), the EPSRC (grant no. EP/R031711/1 to S.J.H. and S.R.), the Henry Royce Institute for Advanced Materials (funded through grant nos. EP/R00661X/1, EP/S019367/1, EP/P025021/1 and EP/P025498/1), and the ISCF Smart Sustainable Plastic Packaging fund (grant no. NE/V01045X/1 with H. Holmes, M. Sharmina, A. Adelekan, T. Holmes). We are grateful to Diamond Light Source for time on beamlines i03, i04 and i04-1 under proposals MX12788-50, MX17773-25, MX17773-34 and MX17773-52, and to Manchester SYNBIOCHEM Centre (grant no. BB/M017702/1) and the Future Biomanufacturing Hub (EP/S01778X/1) for access to their facilities. The Graphical Abstract, Fig. 1 and Supplementary Fig. 9 were created with BioRender.com.
Author information
Authors and Affiliations
Contributions
A.P.G. and E.L.B. designed and directed the research. E.L.B. carried out molecular biology, enzyme characterization, assay development, directed evolution experiments and interpreted and presented the data. E.L.B., R.S. and J.F. carried out protein production and purification and performed biochemical assays. R.S. carried out protein crystallization. P.J.R.D. discussed interpretations of biochemical assays. S.K. and M.P.S. carried out polymer characterization measurements and analysed and presented the associated data. S.R. and S.J.H. performed microscopy and interpreted the data. A.A.T. and A.A.G. carried out substrate milling. F.J.H. and C.L. interpreted, analysed and presented structural data, and carried out molecular docking studies. A.P.G., E.L.B., M.P.S. and S.K. wrote the manuscript. All authors discussed the results and reviewed the manuscript.
Corresponding author
Ethics declarations
Competing interests
The authors declare no competing interests.
Peer review
Peer review information
Nature Catalysis thanks Rey-Ting Guo, Ioannis Pavlidis and the other, anonymous, reviewer(s) for their contribution to the peer review of this work.
Additional information
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Extended data
Extended Data Fig. 1 Overview of the IsPETase directed evolution progression.
The crystal structures represent an overview of the evolution, with the IsPETaseTS protein represented as a turquoise ribbon. The catalytic triad and W185 are shown in ball and stick representation coloured by all atoms, with blue and grey carbon atoms, respectively. The three mutations in IsPETaseTS compared to IsPETaseWT are highlighted as yellow spheres, mutations installed in directed evolution rounds 1-2 as light blue spheres, the rationally inserted additional disulphide bridge (DSB) as black spheres and mutations installed in rounds 3–6 as pink spheres. More details on the evolution outcomes can be found in Supplementary Table 1.
Extended Data Fig. 2 Comparison of reactions with IsPETaseTS and HotPETase over a range of temperatures.
48 h time-courses of cryPET reactions, showing the mean total concentration of released MHET and TPA, with HotPETase (yellow-pink) and IsPETaseTS (blues) over time, using 0.4% cryPET substrate loading (4 g L−1) and 0.29 mg g−1 enzyme loading (0.04 μM). Reactions were performed in pH 9.2, 50 mM Gly-OH buffer, 4% BugBuster, in triplicate, with error bars representing the s.d. of the replicate measurements.
Extended Data Fig. 3 Comparison of reactions with HotPETase and LCCICCG over a range of temperatures.
48 h time-courses of cryPET reactions, showing the mean total concentration of released MHET and TPA, with HotPETase (yellows-pinks) and LCCICCG (greens) over time, at a range of temperatures, using 0.4% cryPET substrate loading (4 g L−1) and 0.29 mg g−1 enzyme loading (0.04 μM). LCCICCG was assayed in its reported optimal operating buffer: pH 8, 100 mM K-Pi; IsPETase and its derivatives were assayed under the library screening buffer conditions: pH 9.2, 50 mM Gly-OH buffer, 4% BugBuster. Reactions were carried out in triplicate, with error bars representing the s.d. of the replicate measurements.
Extended Data Fig. 4 Comparison of reactions with additional enzyme or substrate added.
48 h time-courses showing the mean total concentration of released MHET and TPA, where following reaction with HotPETase at 60 °C for 24 h (pink) (using 0.4% cryPET substrate loading (4 g L−1) and 0.29 mg g−1 enzyme loading (0.04 μM)), either 0.29 mg g−1 fresh enzyme (0.04 μM) (blue) or 4 g L−1 fresh cryPET substrate (yellow) was added. Reactions were performed in pH 9.2, 50 mM Gly-OH buffer, 4% BugBuster, in triplicate, with error bars representing the s.d. of the replicate measurements.
Extended Data Fig. 5 Comparison of HotPETase activity with different substrates at 40 °C and 60 °C under library screening conditions and optimised reaction conditions.
Bar chart showing the mean total concentration of released MHET and TPA accumulated over 3 h (light pink) and 24 h (dark pink) at either 40 °C or 60 °C in reactions using HotPETase with different PET substrates (crystalline PET powder (cryPET), milled bottle-grade PET (bgPET), PET/PE composite film lid (PET/PE), 0.4% total substrate loading (4 g L−1)). Reactions were performed using either library hit screening conditions (A): 0.29 mg g−1 enzyme loading (0.04 μM), pH 9.2, 50 mM Gly-OH, 4% BugBuster or optimised conditions (B): 3.62 mg g−1 enzyme loading (0.5 μM), pH 9.7, 50 mM Gly-OH buffer, 4% BugBuster. Reactions were carried out in triplicate; error bars represent the s.d. of the replicate measurements; each replicate measurement is represented as a black circle.
Extended Data Fig. 6 Comparison HotPETase activity under standard and optimised reaction conditions.
24 h time-courses of reactions conducted at 60 °C with HotPETase, showing the mean percentage of cryPET depolymerized (0.4% cryPET substrate loading (4 g L−1)), calculated using the concentration of MHET and TPA produced. Standard conditions were: 0.29 mg g−1 enzyme loading (0.04 μM), library screening buffer: pH 9.2, 50 mM Gly-OH, 4% BugBuster (dashed line). Optimised reaction conditions were: 3.62 mg g−1 enzyme loading (0.5 μM), pH 9.7, 50 mM Gly-OH, 4% BugBuster (solid line). Reactions were carried out in triplicate; error bars represent the s.d. of the replicate measurements.
Extended Data Fig. 7 Comparison of crystal structures and features of HotPETase and IsPETaseTS.
(a) A global superposition of IsPETaseTS (yellow) and HotPETase (light blue). Mutations in IsPETaseTS compared to IsPETaseWT are highlighted with yellow spheres. Mutations installed during directed evolution are highlighted with pink spheres. The rationally inserted disulphide bridge is highlighted with black spheres. The catalytic triad and W185 are in ball and stick representation coloured by all atoms, with blue and grey carbon atoms, respectively. (b) The disulphide bridge is correctly formed between C233 and C282 in HotPETase. Electron density is 2Fo-Fc contoured at 1 sigma (blue) and 2 sigma (yellow). (c) The conversion of P181 in IsPETaseTS to V181 in HotPETase (highlighted pink) results in extension of β-sheet 6, and the formation of an additional hydrogen bond (dashed lines) to L199. (d) In HotPETase, the wobbling tryptophan (W185, grey sticks), forms a π-stacking interaction (dashed line) with the installed Y214 (pink sticks).
Extended Data Fig. 8 Comparison of HotPETase and HotPETaseLR.
(a) Protein melt curves for HotPETase and HotPETase K212N, E213S, Y214S (HotPETaseLR). Melt curve readings were carried out in triplicate. (b) 24 h time-courses, showing the mean total concentration of released MHET and TPA, in reactions at either 40 °C or 65 °C with either HotPETase or HotPETaseLR, using 0.4% cryPET substrate loading (4 g L−1) and 0.29 mg g−1 enzyme loading (0.04 μM). Reactions were performed in pH 9.2, 50 mM Gly-OH buffer, 4% BugBuster, in triplicate; error bars represent the s.d. of the replicate measurements.
Supplementary information
Supplementary Information
Supplementary Methods, Figs. 1–23, Tables 1–4 and references.
Rights and permissions
About this article
Cite this article
Bell, E.L., Smithson, R., Kilbride, S. et al. Directed evolution of an efficient and thermostable PET depolymerase. Nat Catal 5, 673–681 (2022). https://doi.org/10.1038/s41929-022-00821-3
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1038/s41929-022-00821-3
This article is cited by
-
Functional tailoring of a PET hydrolytic enzyme expressed in Pichia pastoris
Bioresources and Bioprocessing (2023)
-
Discovery and mechanism-guided engineering of BHET hydrolases for improved PET recycling and upcycling
Nature Communications (2023)
-
Investigating the effects of cyclic topology on the performance of a plastic degrading enzyme for polyethylene terephthalate degradation
Scientific Reports (2023)
-
The structural and molecular mechanisms of type II PETases: a mini review
Biotechnology Letters (2023)
-
Efficient depolymerization of polyethylene terephthalate (PET) and polyethylene furanoate by engineered PET hydrolase Cut190
AMB Express (2022)