Open Access Article
Cornelis Post
ab,
George Karchilakis
ab,
Dina Maniar
a,
Vincent S. D. Voet
b,
Rudy Folkersmab and
Katja Loos
*a
aMacromolecular Chemistry & New Polymeric Materials, Zernike Institute for Advanced Materials, University of Groningen, Nijenborgh 3, 9747 AG Groningen, the Netherlands. E-mail: k.u.loos@rug.nl
bCircular Plastics, Academy Tech & Design, NHL Stenden University of Applied Sciences, Van Schaikweg 94, 7811 KL Emmen, the Netherlands
First published on 5th February 2026
2,5-Bishydroxymethyltetrahydrofuran (BHMTHF), also known as 2,5-tetrahydrofurandimethanol (THFDM), is a sugar-derived monomer containing a rigid alicyclic tetrahydrofuran structure. In this study, three series of BHMTHF-based (co)polyesters were enzymatically synthesized using various aliphatic comonomers and the furanic comonomers 2,5-bishydroxymethylfuran (BHMF) and 2,5-furandicarboxylic acid (FDCA). The length of the aliphatic comonomers had a significant effect on the Tg and complex viscosity. Similarly, a higher furan content, either BHMF or FDCA, in the copolyesters increased the Tg values and complex viscosities. Biodegradation experiments in activated sludge demonstrated that all aliphatic-BHMTHF-based polyesters were biodegradable, with rates ranging from 60 to 89% in 28 days. In addition, the furan-BHMTHF-based copolyesters also demonstrated a biodegradable behavior over time, without a significant influence of either the BHMF or FDCA content. Finally, the greenness of the enzymatic synthesis process was assessed based on atom economy (AE), reaction mass efficiency (RME), overall efficiency (OE), E-factor, and EcoScale. This work supports the tuneability of the thermal and rheological properties of BHMTHF-based (co)polyesters and reveals the biodegradability of these materials. This emphasizes that BHMTHF is a very promising biobased rigid monomer for the production of sustainable (co)polyesters.
Green foundation1. The conventional plastic economy relies largely on fossil-based polymers, bio-based polymers are renewable and more sustainable alternatives. Sugar-derived monomers, including BHMTHF, are considered key materials for the development of green polymers.2. The design and application of biodegradable polymers are important to reduce (micro)plastic pollution and accumulation in the environment. BHMTHF-based (co)polyesters are demonstrated to be biodegradable and have tunable properties, which makes BHMTHF a promising monomer for the production of environmentally friendly polyesters. 3. The traditional synthesis process of polyesters involves high temperature and toxic metal-based catalysts. Enzymatic polymerization is an efficient, selective, and low-temperature synthesis process, and is suitable for a wide range of monomers. BHMTHF-based (co)polyesters could be successfully synthesized via a sustainable enzymatic bulk polymerization process in relatively high molecular weight. |
Furthermore, HMF can also be reduced to yield monomers such as 2,5-bishydroxymethylfuran (BHMF), 2,5-bishydroxymethyltetrahydrofuran (BHMTHF), 1,6-hexanediol (HDO), and 1,2,6-hexanetriol (HT).4 Among these, BHMTHF, also reported as 2,5-tetrahydrofurandimethanol (THFDM) and 2,5-dihydroxymethyltetrahydrofuran (DHMTHF), is particularly attractive. Its alicyclic tetrahydrofuran structure in combination with two primary hydroxyl groups makes it structurally similar to BHMF, while providing the additional benefit of a remarkably higher thermal stability compared to its furan-based counterpart.5
This makes BHMTHF, in contrast to BHMF, suitable for high temperature bulk polymerization for the synthesis of diverse polyesters with unique properties. The group of Wei synthesized a variety of BHMTHF-based (co)polyesters via melt polymerization using an L-scale reactor. They synthesized poly(ethylene-co-tetrahydrofurandimethanol terephthalate) (PETT) wherein BHMTHF (THFDM) was demonstrated to be a suitable alternative to replace 1,4-cyclohexanedimethanol (CHDM), which is currently used in the industrial production of poly(ethylene terephthalate-co-cyclohexanedimethanol terephthalate) (PETG).6 In addition, they (co)polymerized BHMTHF with terephthalic acid (TA), FDCA, succinic acid, and adipic acid, which resulted in a polymeric material with a wide range of properties.7–9 The copolyester PETT is popular for fiber applications and was also synthesized by other groups to study melt spinning, electrospinning, crystallization behavior and mechanical performances.10–12 In general, the incorporation of BHMTHF units in copolyesters results in reduced crystallinity or even fully amorphous materials, relatively high Tg values and increased hydrophilicity.13–15 These features are attributed to the rigid tetrahydrofuran ring structure, which contains an electronegative ether group. These unique characteristics of the BHMTHF ring are also recognized in polyurethanes, which demonstrated self-healing behavior due to strong hydrogen bonding between the urethane groups and the oxygen functionality in the BHMTHF units.16–18
Although BHMTHF-based polymers are not extensively studied, it is mainly (co)polymerized with either FDCA or TA, while only succinic acid and adipic acid are used as aliphatic comonomers. Hence, it is important to polymerize BHMTHF with biobased aliphatic comonomers of various sizes to expand the library. In addition, conventional melt polycondensation is currently the only reported synthesis route. Enzymatic polymerization is demonstrated to be a sustainable, efficient and selective tool to produce various biobased polyesters.19–22 In addition, the use of toxic metal-based catalysts and high temperatures are avoided, which follows the Green Chemistry principles about efficient catalysis and less hazardous chemical syntheses. Due to BHMTHF's structural similarity to BHMF, it is expected that enzymatic polymerization could be a viable synthesis route as well.23,24 Furthermore, poly(butylene-co-tetrahydrofurandimethylene succinate) is shown to be prone to enzymatic degradation, which is another indication that enzymatic polymerization might be a promising alternative.9 These results indicate that BHMTHF-based polyesters are prone to biodegradation. Although enzymatic degradation is not the same as biodegradation, where polymers degrade by microorganisms to water, minerals, biomass, and CO2.25 The produced CO2 returns in the carbon cycle, or can be a valuable input for the chemical industry.26
In this work, BHMTHF is enzymatically polymerized with aliphatic comonomers that contain a varying number of methylene units. In addition, the polyester derived from BHMTHF and dimethyl adipate (poly(tetrahydrofurandimethylene adipate)) was copolymerized with either BHMF or diethyl FDCA in varying ratios. The impact of aliphatic spacer length and the furanic content (BHMF or FDCA) on the thermal characteristics, rheology and biodegradability are studied. The results give a broad perspective on the structure–property relationship of BHMTHF units in (co)polyesters.
:
dimethyl ester molar ratio of 1.00
:
1.00, and 10% w/w iCALB was added as a catalyst (Fig. 1). The same scale and catalyst loadings were used for the synthesis of the copolyesters poly(tetrahydrofurandimethylene adipate-co-tetrahydrofurandimethylene 2,5-furandicarboxylate) (PTAd-TF) and poly(tetrahydrofurandimethylene adipate-co-2,5-furandimethylene adipate) (PTAd-FAd)(Fig. 2), and the feed ratios are provided in Table 2.
![]() | ||
| Fig. 1 Enzymatic bulk polymerization of BHMTHF and aliphatic dimethyl esters with a varying number of methylene units x. | ||
The reaction mixture was first maintained at 100 °C for 24 h under a mild argon flow. Then, the temperature was increased to 120 °C, and the system was gently switched to vacuum (2 × 10−2 mbar) and maintained for another 24 h. Finally, the temperature was increased to 130 °C for the last 7 h of the experiment. The obtained polymer was dissolved in chloroform, separated from the enzyme using a needle and syringe, precipitated in diethyl ether, centrifuged (10 min, 4500 rpm) and dried in the vacuum oven at 80 °C for 24 h. Organic solvents were required for purification and product recovery, but could be eliminated at larger scales, where polymers can be directly extruded from the reactor. All synthesized polyesters appeared as a viscous colorless liquid except PTAd-FAd_100, which appeared as a solid. The detailed NMR data of all synthesized polyesters are provided in the SI Fig. S1–S19.
The number average molecular weight (
) and weight average molecular weight (
) were determined via gel permeation chromatography (GPC). The analyses were performed on a Hewlett Packard 1100 device with three MIXED-E columns (Agilent Technologies PL, 300 × 7.5 mm 3 μm) equipped with a GBC 1240 refractive index detector. THF, stabilized with BHT, served as the solvent and eluent at a flow rate of 1 mL min−1 at 40 °C. The polymer samples were prepared at a concentration of 5 mg mL−1, and toluene acted as an internal standard. A conventional calibration curve based on monodispersed polystyrene (PS) standards was used to calculate the relative molecular weights.
The degree of polymerization (DP) of the copolyesters was determined as follows:
![]() | (1) |
The glass transition temperatures (Tg) and the melting points (Tm) of the polymers were determined by modulated differential scanning calorimetry (mDSC) analysis. A TA-Instruments Q1000 DSC was used to subject the samples (5–6 mg) to a heat-cool-heating cycle ranging from −70 to 150 °C under a nitrogen atmosphere. The average heating rate was set to 3 °C min−1 with a temperature modulation period of 60 s and an amplitude of 0.50 °C.
![]() | (2) |
AE was determined from the reaction stoichiometry as the ratio between the molecular weight of the ideal repeating unit and the total molecular weight of all reactants entering the polymer backbone, assuming methanol or ethanol to be the only stoichiometric by-products (eqn (3)). RME was obtained by dividing the mass of the isolated polymer by the total mass of all reactants, and incorporates, therefore, the yield and non-stoichiometric excess of BHMTHF or diester(eqn (4)). OE is defined as the ratio between RME and AE and was used as an integrated measure of the transformation efficiency (eqn (5)).
![]() | (3) |
![]() | (4) |
![]() | (5) |
The E-factor was calculated as the mass ratio of all waste generated to the mass of isolated (co)polyester (eqn (6)). In accordance with common practice, water was excluded from the E-factor calculations, whereas all organic solvents, immobilized enzyme, and other auxiliaries used during the polymerization and work-up were counted as waste.33 Hence, the reported E-factors represent conservative laboratory-scale values that do not account for solvent recycling or enzyme reuse.
![]() | (6) |
EcoScale scores were determined using the semi-quantitative methodology proposed by Van Aken et al., in which an ideal score of 100 is reduced by penalty points associated with low yields, hazardous or expensive reagents and catalysts, non-preferred solvents, high temperatures, long reaction times, and demanding work-up.31 The input parameters for the EcoScale calculations (yields, reagents, solvent types, temperature, and reaction time) were taken directly from the experimental procedures used for each polymerization.
), weight average molecular weight (
), polydispersity (Đ), degree of polymerization (DP), glass transition temperature (Tg), and 5% and 50% decomposition temperatures (Td5%, Td50%)
The number average molecular weight (
) ranged from 5500 to 11
200 g mol−1, corresponding to a degree of polymerization (DP) ranging from 26 to 41. The use of DMSuc and DMPim as comonomers resulted in slightly lower
and DP values, expected due to lower reaction kinetics, which was also observed in our previous work about BHMF-based polyesters.29
The second series involves copolyesters consisting of BHMTHF, BHMF, and DMAd, wherein the BHMTHF content was gradually increased at the cost of BHMF content (Table 2a). The
values varied from 6600 to 11
000 g mol−1 and there was no significant effect of the BHMTHF/BHMF content on the molecular weight of the copolyesters. This implies a similar reactivity of BHMTHF and BHMF toward DMAd during enzymatic polymerization with iCALB. However, the polyester consisting of only BHMF (PTAd-FAd_100) demonstrated a lower
compared to the pure polyester from BHMTHF and DMAd (PTAd-FAd_00, or PTAd). Noteworthily, the polymerization reactions started at 100 °C, while the synthesis of BHMF-based homopolyesters was initiated at 70 °C in our previous work due to BHMF's limited thermal stability.29,34 The possibility of starting the polymerization at a higher temperature was attributed to a higher purity of the BHMF used in this study. BHMF is commonly derived from the thermally less stable intermediate HMF, and trace amounts might influence the overall thermal stability.35
), weight average molecular weight (
), polydispersity (Đ), degree of polymerization (DP), glass transition temperature (Tg), melting temperature (Tm), and 5% and 50% decomposition temperatures (Td5%, Td50%)
| (a) Polymer | BHMF feed (%) | BHMF polymer (%) | (g mol−1) | (g mol−1) | Đ | DP | Tg (°C) | Tm (°C) | Td5% (°C) | Td50% (°C) |
|---|---|---|---|---|---|---|---|---|---|---|
| PTAd-FAd_100 | 100 | 100 | 6600 | 10 800 |
1.6 | 28 | −18.8 | 65.5 | 271 | 293 |
| PTAd-FAd_75 | 75 | 74 | 9800 | 15 200 |
1.5 | 41 | −22.0 | 43.6 | 276 | 305 |
| PTAd-FAd_50 | 50 | 50 | 10 500 |
17 500 |
1.7 | 44 | −23.3 | — | 276 | 370 |
| PTAd-FAd_25 | 25 | 24 | 8600 | 16 600 |
1.9 | 36 | −24.8 | — | 298 | 375 |
| PTAd-FAd_00 | 0 | 0 | 11 000 |
17 900 |
1.6 | 45 | −27.5 | — | 303 | 365 |
| (b) Polymer | FDCA feed (%) | FDCA polymer (%) | (g mol−1) | (g mol−1) | Đ | DP | Tg (°C) | Tm (°C) | Td5% (°C) | Td50% (°C) |
|---|---|---|---|---|---|---|---|---|---|---|
| PTAd-TF_100 | 100 | — | <500 | <500 | — | — | — | — | — | — |
| PTAd-TF_75 | 75 | 69 | 1000 | 1300 | 1.3 | 4 | −3.0 | — | 267 | 385 |
| PTAd-TF_50 | 50 | 53 | 4600 | 7100 | 1.6 | 18 | −4.5 | — | 332 | 392 |
| PTAd-TF_25 | 25 | 29 | 8500 | 15 100 |
1.8 | 35 | −9.0 | — | 338 | 394 |
| PTAd-TF_00 | 0 | 0 | 9100 | 17 200 |
1.9 | 38 | −29.9 | — | 322 | 393 |
A different phenomenon was observed in the third series, which covered copolyesters based on BHMTHF, DEFDCA, and DMAd (Table 2b). The
values decreased significantly for higher contents of DEFDCA in the feed. In addition, the enzymatic polymerization of only BHMTHF and DEFDCA was unsuccessful since only oligomer formation was observed. This is attributed to the limited enzymatic activity towards polymerization of two cyclic monomers, e.g., FDCA and BHMTHF. This substrate limitation effect of the active site of iCALB was also observed for copolyesters based on dimethyl FDCA, BHMF, and aliphatic diols.21
It is worth noticing that iCALB easily polymerizes BHMTHF with DMAd, but FDCA with BHMTHF does not even result in oligomers under the same conditions, while BHMTFH and FDCA contain both a five-membered ring structure. This lipase consists of a Ser-His-Asp catalytic triad, which is surrounded by a relatively large hydrophobic pocket to allow absorption on hydrophobic surfaces, a mechanism called interfacial activation.36,37 The catalytic transesterification mechanism involves first the incorporation and activation of the carbonyl group in the active site and subsequently the liberation of the alcohol group, as described in detail by Hevilla et al. (2021).38 This is followed by the nucleophilic attack of another primary alcohol group and the release of the product with the newly formed ester bond.20,22 This means that the chemical structure and bulkiness of the diacid, dimethyl, or diethyl ester is key to interacting and fitting in the active site and thus the possibility of polymerization. In addition, the results in this work demonstrate that the bulkiness of the diol, i.e., BHMTHF or BHMF, has no significant limitation.
Although iCALB has difficulties with polymerization of two cyclic monomers, it proved to be a very selective and efficient catalyst at relatively low temperature, which makes it an advantageous tool for monomers with limited thermal and chemical stability, such as BHMF, and avoids the use of toxic metal-based catalysts and solvents. This aligns with the principles of Green Chemistry related to less hazardous chemical syntheses, designing safer chemicals, and efficient catalysis.
The polymer structures were confirmed by NMR analysis. The 1H-NMR spectrum of PTAd, named as PTAd-TF_00 and PTAd-FAd_00 in the two copolyester series, is provided as a representative example and depicted in Fig. 3. The spectra of the other BHMTHF-based polyesters are provided in the SI (Fig. S1–S6). The 13C-NMR, COSY, HSQC, and HMBC spectra (SI, Fig. S7–S10) were used to assign all protons to their corresponding signals in the 1H-NMR spectrum, due to overlapping signals of the protons “3” and “4” of the tetrahydrofuran ring, caused by the presence of the chiral carbons. The polymerization was confirmed by the substantial decrease of BHMTHF hydroxyl groups (“1”) and methoxy groups of DMAd (“7”), and the appearance of the protons next to the formed BHMTHF ester group (“3” and “4”).
![]() | ||
| Fig. 3 1H-NMR spectrum of poly(tetrahydrofurandimethylene adipate) (PTAd, PTAd-TF_00, PTAd-FAd_00) in DMSO-d6. | ||
The furan content of the copolyesters, either BHMF or FDCA content, was derived from 1H-NMR spectra as well, which are provided in the SI (Fig. S11–S19). In case of the BHMF-based copolyesters, the integrated signals of the CH2 groups of the furan next to the ester bond (“8”) and the similar peaks of BHMTHF units (“3” and “4”) were used to determine the actual furan content in the copolymers (eqn (7)). The FDCA content was derived from the integrated BHMTHF peaks “3” and “4” for the BHMTHF-DMAd segments, and similar signals at slightly higher ppm for the BHMTHF-FDCA segments (“8” and “9”) (eqn (8)).
The results are provided in Table 2a and b, and reveal that the feed ratios are similar to the final ratios in the case of the BHMF-BHMTHF-based and FDCA-BHMTHF-based copolyesters. The oligomer PTAd-TF_75 yielded a furan ratio of 69%, however this value is underestimated due to the presence of relatively large DEFDCA end groups that overlap with the BHMTHF ester bonds.
![]() | (7) |
![]() | (8) |
The thermal behavior of the polyesters was analyzed by modulated DSC experiments. The Tg values of the BHMTHF-based polyesters from the first series were obtained from the second reversing heating ramp to prevent interference with the relaxation enthalpy. Fig. 4 demonstrates the decreasing quadratic behavior of the Tg values as a function of the aliphatic spacer, i.e., the number of methylene units in the aliphatic comonomer. A longer aliphatic spacer length increases chain flexibility and mobility, while steric hindrance decreases due to the relatively lower BHMTHF content for a higher number of methylene units. This thermal behavior is very similar to the BHMF-based polyesters that are synthesized with the same aliphatic comonomers; only the absolute Tg values of the BHMF-based polyesters are approximately 20 °C higher. This difference is attributed to the planar and aromatic structure of BHMF, which is absent for BHMTHF.
![]() | ||
| Fig. 4 Tg values of BHMTHF- and BHMF-based polyesters containing different numbers of methylene units in the comonomer segment, and the structural representations of the polyesters. Data of the BHMF-based polyesters is obtained from previous work.29 | ||
All BHMTHF-based polymers from the first series lack a melting endotherm and are therefore completely amorphous. This corresponds well with the literature, for PTSuc and PTAd, respectively, and their appearance as a viscous liquid.8 The lack of crystallinity was attributed to the rigidity of the ring structure of BHMTHF, which disrupts interactions between the chains.15
The Td5% and Td50% of the two series of copolyesters are given in Table 2a and b for the BHMF and FDCA-based copolyesters, respectively. The thermal stability of the BHMF-based copolyesters (PTAd-FAd) increased for higher BHMTHF content, as represented by the Td5% values. In addition, these copolyesters demonstrated a twostep degradation profile (Fig. S21), which corresponded well with the degradation profiles of the pure polyesters and could be linked to the composition of the copolyesters.
The thermal stabilities of the FDCA-based copolyesters were all relatively high and similar in magnitude. However, the oligomer PTAd-TF_75 demonstrated a lower Td5% value, which is attributed to its significantly lower molecular weight.
The thermal behavior of the two series of BHMTHF-based copolyesters are depicted in Fig. 5. The Tg values of the BHMF-BHMTHF-based copolyesters increased linearly with a higher furan content as a result of increased structural rigidity. In other words, the Tg values of the copolyesters align well between the values of the two homopolyesters PTAd-FAd_100 (−19 °C) and PTAd-FAd_00 (−28 °C), and correspond well with literature values of the same homopolyesters, −13 and −33 °C, respectively.8,29
The Tg values of the FDCA-BHMTHF-based copolyesters increased more drastically for a higher furan content. This behavior is expected due to the high Tg value of the homopolyester PTAd-TF_100 (poly(2,5-tetrahydrofurandimethanol 2,5-furandicarboxylate) (PTF)), which could not be enzymatically synthesized, but literature reported values around 75 °C.7,13 The Tg value of the oligomer PTAd-TF_75 is included, however, is expected to be on the low side due to the limited molecular weight.
The BHMF-based polyester PFAd, synthesized in our previous work, is known to be a semicrystalline material with a relatively low Tm (63 °C).29 This Tm (65 °C) was also observed in the first heating ramp of the same polyester (PTAd-FAd_00) in this work (Fig. S26). In addition, the copolyester PTAd-FAd_25 also demonstrated a Tm (44 °C), and was considerably lower in magnitude, which indicated a significant reduction in degree of crystallinity. None of the other copolyesters, from both series, demonstrated a melting endotherm, attributed to BHMTHF's ability to hinder crystallization.7
The modulated DSC curves of the second reversing heating ramps of all BHMTHF-based (co)polyesters are provided in the SI (Fig. S23–S25).
The same rheology experiments were performed on the two series of copolyesters. The low frequency complex viscosities were derived from the frequency sweeps (Fig. S27 and S28), and are plotted here versus the furan content, either BHMF or FDCA. Fig. 6c visualizes that the incorporation of FDCA results generally in higher strength materials with respect to the BHMF-based copolyesters, which aligns with the Tg results. In addition, in both cases, a higher furan content resulted in higher viscosities. The copolyester PTAd-TF_75 is an outlier in this trend; however, the low strength was attributed to its low molecular weight
. The polymers PTAd-TF_100 and PTAd-FAd_100 demonstrated a very similar viscosity, which is expected given that they are structurally identical polyesters (PTAd) with similar
. The polymer PTAd-FAd_100 was not subjected to the rheology measurements, since its Tm (65 °C) is higher than the experimental temperature (40 °C). PTAd-FAd_75 was also observed as a semi-crystalline material (Tm = 44 °C), but its melting endotherm was very low in magnitude and the material behaved like a viscoelastic material during the strain and frequency sweeps. Therefore, this data point is still included in Fig. 6c, but could have been influenced by minor crystalline phases in the material during the measurement.
In summary, the rheological behavior of the BHMTHF-based (co)polyesters was demonstrated to be tunable by varying the number of methylene units or the furan content. In addition, it indicates their behavior during (re)processing and confirms their recyclability to prevent waste and increase their sustainability.
Fig. 7a demonstrates the percentage of biodegradation versus time for the first series of BHMTHF-based polyesters, and supports this theory. All these polyesters demonstrated a clear biodegradation behavior over time in activated sludge. The percentage of biodegradation of days ranged from 60 to 89%, while there was no discernible relationship observed between the chemical structure and degree of biodegradation.
The biodegradation behavior of the BHMF-BHMTHF-based copolyesters is depicted in Fig. 7b. All copolyesters were partially degraded in the active sludge, and the percentage of biodegradation ranged from 60 to 78%. Similar results are obtained from the FDCA-BHMTHF-based polyesters, which resulted in biodegradation rates ranging from 44 to 81% (Fig. 7c). In both series, the copolyester composition did not influence the biodegradation performances significantly. This is attributed to the amorphous morphology and low Tg values of all these copolymers, implying a similar physical appearance.
The pure BHMF-based polyester PTAd-FAd_100 (PFAd) demonstrated a remarkably lower degree of biodegradation (8%) compared to the copolyesters, while the biodegradation result of the same polyester in our previous work was also higher (22%).29 The difference regarding the BHMF-BHMTHF-based copolyesters is attributed to the differences in crystallinity. PTAd-FAd_100 demonstrated a clear melting peak, while PTAd-FAd_75 showed only a small melting endotherm and the other copolyesters were completely amorphous (Table 2). The lower percentage of biodegradation with respect to our previous result of the same polyester is explained by a difference in surface area. In this work, all viscous polymers were attached to the stirring bar at the start of the experiments, while PTAd-FAd_100 was first melted and subsequently also attached to the stirring bar for consistency in surface area. In our previous work, all polyesters were added as a fine powder, implying a higher surface area and enhanced biodegradation.
All polymers are measured in duplicate, except for the polymers highlighted (*) due to technical failure of the setup. However, the simplex data of these polymers are in line with expectations and the other polymers tested in duplicate, and are therefore still considered to give a good estimation of the biodegradation behavior. The minor fluctuations in the obtained BOD values and calculated percentages of biodegradation are attributed to relatively small variations in the surrounding temperature during the experiments.
In summary, the percentage of biodegradation after 28 days ranged from 44 to 89% for all BHMTHF-based (co)polyesters, and can therefore be considered biodegradable. This is in line with expectations due to their similarities with biodegradable BHMF-based polyesters and their amorphous morphology.29 The biodegradability of these polymers prevents the formation and accumulation of microplastics, which aligns with the principles of Green Chemistry about waste prevention, safer chemicals, design of degradation, and pollution prevention.
| Polymer | AE (%) | RME (%) | OE (%) | E-factor (kg/kg) | EcoScale |
|---|---|---|---|---|---|
| (a) | |||||
| PTSuc | 77 | 48 | 62 | 84 | 67 |
| PTGlu | 78 | 60 | 77 | 67 | 75 |
| PTAd | 79 | 58 | 73 | 69 | 73 |
| PTPim | 80 | 50 | 62 | 81 | 64 |
| PTSub | 81 | 49 | 61 | 82 | 64 |
| PTAze | 82 | 49 | 60 | 82 | 63 |
| PTSeb | 82 | 54 | 66 | 74 | 69 |
| (b) | |||||
| PTAd-FAd_100 | 79 | 56 | 71 | 73 | 72 |
| PTAd-FAd_75 | 79 | 56 | 71 | 73 | 71 |
| PTAd-FAd_50 | 79 | 56 | 71 | 72 | 72 |
| PTAd-FAd_25 | 79 | 48 | 61 | 85 | 66 |
| PTAd-FAd_00 | 79 | 55 | 70 | 74 | 71 |
| (c) | |||||
| PTAd-TF_100 | 73 | — | — | — | — |
| PTAd-TF_75 | 75 | 49 | 66 | 82 | 61 |
| PTAd-TF_50 | 76 | 49 | 64 | 83 | 60 |
| PTAd-TF_25 | 78 | 53 | 69 | 76 | 65 |
| PTAd-TF_00 | 79 | 59 | 74 | 69 | 68 |
A similar picture emerges for the BHMF-BHMTHF-based copolyesters (PTAd-FAd series). Introduction of BHMF resulted in similar AE (79%) relative to the purely aliphatic PTAd, as expected from the similarities in molecular weight between BHMF and BHMTHF. In addition, RME (48–56%) and OE (61–71%) remain comparable to those of the homopolyesters due to similarities in yield. The E-factors ranged from 72 to 84 and were of similar magnitude as the aliphatic homopolymers due to an identical experimental procedure. EcoScale scores of 66 to 72 again classify these syntheses as “acceptable”, with no significant influence of the BHMF content.
For the FDCA-BHMTHF-based copolyesters (PTAd-TF series), the metrics highlight both strengths and clear opportunities for further improvement. In the case of the FDCA-BHMTHF polymer (PTAd-TF_100), only the AE is presented since the enzymatic polymerization was unsuccessful for these two cyclic monomers, and the obtained oligomers would represent unrealistic values for the other green metrics.
All other copolyesters in this series (PTAd-TF_75–PTAd-TF_00) show AE values of roughly 75 to 79%, RME values of 49 to 59% and OE in the range of 64 to 74%, with E-factors of 69 to 83 and EcoScale scores of 60 to 68. This shows that partial substitution of adipate by FDCA, enabling higher glass transition temperatures, complex viscosities, and expected improved barrier properties as reported for related furanic copolyesters,44 can be achieved without a significant penalty in the reaction-level green metrics.
This highlights that the distribution of AE, RME, OE, E-factors, and EcoScale values across the PTAd-TF and PTAd-FAd series becomes essentially indistinguishable from that of the BHMTHF homopolyesters. This underlines that the entire BHMTHF-based (co)polyester family can be accessed via protocols that are consistently in the “acceptable” EcoScale range and comparable in performance.
These values are in line with, and in several cases slightly better than, those reported recently for enzymatic bulk polycondensation of BHMF-based polyesters using the same immobilized CALB catalyst and very similar work-up procedures. This resulted in AE values around 77 to 82%, E-factors on the order of 98 to 161 and EcoScale scores between 62 and 73 for the synthesis of BHMF-based polyesters.29
A meaningful benchmark for the green advance of the present work is provided by the state-of-the-art preparation of BHMTHF-based polyesters via conventional melt polycondensation. Jin and co-workers demonstrated the synthesis of various BHMTHF-based polyesters at the kilogram scale using a titanium catalyst up to 240 °C under high vacuum and with multiple steps for pre-polymer formation and removal of low-molecular-weight by-products.8 Although green metrics were not reported, the use of metal catalysts, high reaction temperatures, extended reaction times, and additional purification steps inherently increases energy consumption and the mass of auxiliaries, and would be expected to result in significantly higher E-factors and lower EcoScale scores than those obtained for the mild enzymatic bulk polymerizations described here.45 In contrast, the present method operates at substantially lower temperatures, avoids any metal catalyst, and relies on a recyclable biocatalyst in a solvent-free reaction medium, which directly addresses several of the “Measuring Green Chemistry: Methods, Models, and Metrics” criteria highlighted for greener polymer syntheses.43
At the same time, the metrics analysis clearly identifies the main hotspots of the current laboratory procedure. Across all polymerizations, the E-factor is dominated by the organic solvents used for precipitation, washing, and enzyme removal, rather than by the reagents themselves. This is consistent with quantitative studies showing that solvent use and work-up typically contribute the majority of the mass intensity and environmental burden in polymer synthesis.29 In an industrial context, replacing chlorinated solvents with greener alternatives, minimizing the number of work-up steps and implementing solvent recycling or direct melt processing (for example, via extrusion of the crude polymer) would therefore be expected to reduce the effective E-factor by approximately an order of magnitude and move the EcoScale scores towards the “excellent” regime.
This work aligns with key Green Chemistry principles: the use of renewable feedstocks (7) such as sugar-derived monomers BHMTHF, BHMF, and FDCA; enzymatic catalysis (9) replacing metal catalysts; and energy-efficient, solvent-free bulk polymerization (6) under mild conditions. The resulting biodegradable materials (10) support circularity and environmental compatibility. Minor deviations occur in atom economy (2) due to methanol/ethanol release from ester monomers and in auxiliaries (5) through limited use of chloroform and diethyl ether for purification. Overall, the study exemplifies a renewable, catalytic, and degradable polymer synthesis consistent with the Green Chemistry framework.
:
trans ratio of 90.6
:
9.4 for the enzymatic polymerization of various (co)polyesters. In the first series, BHMTHF was reacted with various aliphatic comonomers to obtain amorphous materials with a relatively high molecular weight, having a
ranging from 5500 to 11
200 g mol−1. The second series consisted of copolyesters derived from BHMTHF, DMAd, and BHMF, wherein the BHMF-BHMTHF ratio was varied. Similarly, the third series consisted of copolyesters derived from BHMTHF, DMAd, and FDCA units, wherein the DMAd-FDCA ratio was altered. The BHMF-based copolyesters reached relatively high
values (6600–11
000 g mol−1), while the enzyme iCALB had difficulties catalyzing the high FDCA content copolyesters, leading to lower
ranging from 1000–9100 g mol−1.
DSC analysis demonstrated that a higher aliphatic spacer length in the first series resulted in a quadratic decrease in Tg values from −8 to −49 °C. Furthermore, a higher BHMF or FDCA content increased the Tg values of the copolyesters, this phenomenon was more pronounced in the FDCA-BHMTHF-based copolyesters.
Rheological analysis demonstrated that polyesters from the first series behave like Newtonian fluids, and the low shear viscosity decreased with an increase in aliphatic spacer length. The low shear viscosity increased with a higher furan content, which indicated that both BHMF and FDCA increased the strength of these materials.
Finally, biodegradation tests revealed that all BHMTHF-based (co)polyesters are prone to biodegradation in activated sludge. The aliphatic spacing length, BHMF, or FDCA content had no significant influence on the biodegradation performances due to their amorphous morphology and chemical similarities.
The greenness of the enzymatic synthesis of all BHMTHF-based (co)polyesters was evaluated based on AE, RME, OE, E-factor, and EcoScale. The polymer composition had no significant effect on the green characteristic metrics of these copolyesters, which were all assessed as “acceptable” according to the EcoScale criteria.
This study demonstrates the compatibility of BHMTHF to be used for various (co)polyesters featuring unique and tunable thermal and rheological properties. This paves the way for BHMTHF to be further explored and utilized as a renewable, rigid biobased monomer in a sustainable plastic economy.
In addition, we want to acknowledge Hero Jan Heeres and Léon Rohrbach, from the Engineering and Technology Institute Groningen (ENTEG), University of Groningen, The Netherlands, for allowing us to use their GPC facilities.
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