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. 2025 Feb 1;18(3):e202400698.
doi: 10.1002/cssc.202400698. Epub 2024 Nov 6.

In-Situ Product Removal for the Enzymatic Depolymerization of Poly(ethylene terephthalate) via a Membrane Reactor

Affiliations

In-Situ Product Removal for the Enzymatic Depolymerization of Poly(ethylene terephthalate) via a Membrane Reactor

Christian Ayafor et al. ChemSusChem. .

Abstract

Poly(ethylene terephthalate) (PET) is a common single-use plastic and a major contributor to plastic waste. PET upcycling through enzymatic depolymerization has drawn significant interests, but lack of robust enzymes in acidic environments remains a challenge. This study investigates in-situ product removal (ISPR) of protons and monomers from enzymatic PET depolymerization via a membrane reactor, focusing on the ICCG variant of leaf branch compost cutinase. More than two-fold improvements in overall PET depolymerization and terephthalic acid yields were achieved employing ISPR for an initial PET loading of 10 mgPET mlbuffer -1. The benefit of ISPR was reduced for a lower initial loading of 1 mgPET mlbuffer -1 due to decreased need for pH stabilization of the enzyme-containing solutions. A back-of-envelop analysis suggests that at a modest dilution ratio, ISPR could help achieve savings on caustic base solutions used for pH control in a bioreactor. Our study provides valuable insights for future ISPR developments for enzymatic PET depolymerization, addressing the pressing need for more sustainable solutions towards plastic recycling and environmental conservation.

Keywords: Enzymatic depolymerization; In-situ product; Membrane reactor; Poly(ethylene terephthalate); Recycling.

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Conflict of interest statement

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Figures

Figure 1
Figure 1
(a) Degradation efficiency and yields of (b) TPA, (c) MHET, and (d) BHET from enzymatic depolymerization of Ex‐RPET under different enzyme concentrations. The theoretical maximum TPA yield for 30 mg of Ex‐RPET was approximately 25.9 mg (i. e., 86.4 % of the mass of Ex‐RPET). Error bars are a single standard deviation of the experiments repeated in triplicates. Experimental conditions: initial substrate concentration ([S]) of 10 mgPET mlbuffer −1, enzyme concentration ([E]) of 0.5, 1, 2, and 3 μM purified LCCICCG (corresponding to 1.45, 2.9, 5.8, and 8.7 mgenzyme gPET −1, respectively), reaction temperature of 55 °C, and 100 mM potassium phosphate buffer at pH of 8.
Figure 2
Figure 2
Comparison of (a) overall PET degradation efficiency, (b) TPA, (c) MHET, and (d) BHET yields from the enzymatic depolymerization of Ex‐RPET for DRs 0 and 4.5. For experiments of DR at 4.5, both ISPR (with the membranes) and non‐ISPR experiments (without the membranes) were conducted. Experimental conditions: initial enzyme to substrate ratio of 2.9 mgenzyme gPET −1, reaction temperature of 55 °C, and 100 mM potassium phosphate buffer at pH≈8. Error bars are a single standard deviation of three repeated experiments.
Figure 3
Figure 3
Comparison of degradation efficiency and solution pH values from the enzymatic depolymerization of Ex‐RPET for (a) (c) initial substrate and enzyme concentrations of 1 mgPET mlbuffer −1 and 0.1 μM purified LCCICCG, respectively, at DRs of 0, 4.5, and 67 and (b) (d) initial substrate and enzyme concentrations of 10 mgPET mlbuffer −1 and 1 μM purified LCCICCG, respectively, at DRs of 0, 4.5, 7, and 67. Experimental conditions: initial enzyme to substrate ratio of 2.9 mgenzyme gPET −1, reaction temperature of 55 °C, and 100 mM potassium phosphate buffer at pH≈8. Error bars are a single standard deviation of three repeated runs. For membrane experiments, the reported pH values were those measured inside the membrane cassettes.
Figure 4
Figure 4
Comparison of (a) TPA (theoretical maximum TPA yield 25.9 mg), (b) MHET, and (c) BHET yields from the enzymatic depolymerization of Ex‐RPET for DRs of 0, 4.5, 7, and 67. Experimental conditions: initial enzyme to substrate ratio of 2.9 mgenzyme gPET −1, [S]=10 mgPET mlbuffer −1, [E]=1 μM purified LCCICCG, reaction temperature of 55 °C, and 100 mM potassium phosphate buffer at pH≈8. Error bars are a single standard deviation of three repeated experiments.
Figure 5
Figure 5
Estimated ratios of NaOH use comparing ISPR to the control (non‐ISPR) environments as functions of dilution ratio and initial PET loading (where pH in the bioreactor is assumed to be controlled at 7.5).

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