Skip to main content

Optimizing operational parameters for the enzymatic production of furandicarboxylic acid building block

Abstract

Background

2,5-Furandicarboxylic acid (FDCA) is a precursor for green plastics due to its structural similarity to terephthalic acid, a common precursor of oil-derived polymers, and its potential production from sugars obtained from plant biomass. Hydroxymethylfurfural oxidase (HMFO) has been reported as a promising biocatalyst for FDCA production since it can convert bio-based 5-hydroxymethylfurfural (HMF) into FDCA building block. This three-step oxidation reaction occurs through the diformylfuran and 2,5-formylfurancarboxylic acid (FFCA) intermediates. Several efforts have been made for the development of HMFO variants that increase FDCA yields by improving their activities over the reaction intermediates. However, there is still limited insight into how operational conditions can influence these enzymatic reactions. The setup of optimal reaction conditions would enable to understand potential problems hampering the effective industrial production of this bioplastic precursor using HMFO as biocatalyst.

Results

In this work, several parameters affecting the performance of Methylovorus sp HMFO oxidizing HMF have been analyzed for the wild-type enzyme, and its V367R and W466F single variants, V367R/W466F double variant, and I73V/H74Y/G356H/V367R/T414K/A419Y/A435E/W466F (8BxHMFO) octuple variant. Our results show how the oxidation of HMF by HMFO enzymes is highly influenced by pH, with different optimal pH values for the different improved variants. Moreover, the enzymes are not stable at high hydrogen peroxide concentrations and their activity is inhibited by the FFCA intermediate in a pH-dependent way. These limitations can be efficiently overcome with the addition of catalase to the reaction medium, which removes the hydrogen peroxide formed during the oxidations, and the controlled dosage of the substrate to limit the amount of FFCA accumulated in the reaction. The different behavior of wild-type HMFO and its variants against pH, hydrogen peroxide and FFCA highlights the importance of considering each variant as an individual enzyme with its own operational conditions for an eventual industrial FDCA production.

Conclusions

This work provides information of those parameters that condition a high production of FDCA by HMFO. Unraveling these factors allowed to increase the FDCA yields by using the most stable enzymes at their optimal pH for HMF oxidation, removing the peroxide with catalase, and avoiding FFCA accumulation by controlling substrate and/or enzyme concentration. These above findings will be useful when planning a future scale-up of these conversions and will provide new viewpoints for the design of HMFO variants that render a more effective performance during HMF conversion into FDCA.

Background

A 2017 global analysis estimated in over 8000 million tons the total amount of virgin plastics produced by the petrochemical industry [1]. This production generated high greenhouse gas emissions from non-renewable fossil resources, and caused both land and water pollution due to limited recycling. Substitution of these oil-based plastics with biodegradable polymers derived from renewable raw materials is thus necessary for the development of a sustainable bio-economy [2]. One of the most promising bio-based plastic polymers is poly(ethylene-2,5-furandicarboxylate) (PEF) [3, 4]. PEF can be used as a green substitute for conventional poly(ethylene-terephthalate) (PET) due to its similar, or even better, properties [5, 6]. The interest of PEF lies in its composition, as it is formed by esterification of ethylene glycol with the renewable building block 2,5-furandicarboxylic acid (FDCA), which can be obtained from sugars derived from lignocellulosic biomass [7, 8].

The processes for FDCA production from lignocellulosic feedstocks usually comprise two steps. First, monosaccharides (generally fructose) derived from plant polysaccharides are dehydrated to form the platform chemical 5-hydroxymethylfurfural (HMF). Second, HMF is converted into FDCA through three consecutive oxidation steps, involving its alcohol and aldehyde groups, that firstly yield diformylfuran (DFF) or hydroxymethylfurancarboxylic acid (HMFCA), respectively, and then formylfurancarboxylic acid (FFCA) as reaction intermediates (Fig. 1) [9, 10]. Different chemical methods have been described for HMF conversion into FDCA, however, they typically lead to low yields and selectivities, and require high temperatures and pressures and the use of metal salts and organic solvents that render the process expensive and polluting [11, 12]. Thus, in the context of green industry, biocatalytic alternatives to these processes are highly interesting, since the reactions can be performed under environmentally-friendly conditions using mild and biodegradable catalysts [13].

Fig. 1
figure1

5-Hydroxymethylfurfural (HMF) conversion into 2,5-furandicarboxylic acid (FDCA). Possible routes, via 2,5-diformylfuran (DFF) or 2,5-hydroxy-methylfurancarboxylic acid (HMFCA) intermediates, to obtain 2,5-formylfurancarboxylic acid (FFCA) and FDCA are shown. Reactions catalyzed by hydroxymethylfurfural oxidase (HMFO) and by aryl-alcohol oxidase (AAO) are indicated with full arrows. FFCA oxidation by AAO in combination with catalase (decomposing the H2O2 generated during the reaction) is also shown [25]

A variety of studies have been performed for the production of FDCA using both enzymatic and whole-cell catalysis [8, 14, 15]. With this aim, several oxidative enzymes have been suggested for the production of FDCA from HMF. However, because most of them are limited to either aldehyde or alcohol oxidation, multi-enzymatic cascades are usually required to complete the reaction [16,17,18,19,20,21,22]. This often limits the overall yield of the process since a consensus between the operational conditions of each enzyme needs to be established. Up to now, only two enzyme types—hydroxymethylfurfural oxidase (HMFO) from Methylovorus sp MP688 [23] and Pseudomonas species [24], and aryl-alcohol oxidase (AAO) from Pleurotus eryngii [25]—have been reported to carry out the three oxidation steps for HMF conversion into FDCA. Both are FAD-containing enzymes of the glucose-methanol-choline oxidase/dehydrogenase (GMC) superfamily [26] with activity on both primary aryl alcohols and hydrated aryl aldehydes. Due to their preference for alcohol substrates, they oxidize HMF into FDCA through the DFF and FFCA intermediates (Fig. 1). However, several characteristics would confer HMFO advantages for the industrial production of FDCA, compared to AAO. First, the bacterial HMFO can be easily overexpressed in Escherichia coli in a soluble active form [24, 27], in contrast to fungal AAO that is typically produced as inclusion bodies in E. coli hosts and thus requires in vitro activation [28] (a time and money consuming process). Nevertheless, the soluble production of P. eryngii AAO using Komagataella pastoris (syn. Pichia pastoris) has been recently reported [29], although a more detailed analysis of the effect of its hyper-glycosylation on furfural oxidation is required. Second, the oxidation of FFCA, which constitutes the limiting step for the enzymatic production of FDCA from HMF, is more efficient for HMFO, since FFCA oxidation by AAO requires long reaction times and is highly inhibited by H2O2 [25]. In addition, HMFO production has been recently upscaled in a cost-effective bioreactor process [30], a crucial factor when considering its industrial application as a biocatalyst.

Due to its promising use for FDCA production, structural and mutagenic studies of the active site of Methylovorus HMFO by Dijkman et al. [31] led to identify the V367R, W466F and V367R/W466F variants as improved biocatalysts. These engineered enzymes perform a faster oxidation of FFCA, the rate-limiting reaction in HMF conversion, than the wild type (WT) enzyme. Moreover, by combining computational prediction and gene shuffling approaches, a multiple variant (8BxHMFO) with eight mutations (I73V/H74Y/G356H/V367R/T414K/A419Y/A435E/W466F) was designed in subsequent studies as a more robust and stable enzyme during catalysis [32]. However, studies on the operational conditions for HMF oxidation into FDCA (using the above HMFO WT and derived variants) are scarce, and a focused analysis of their behavior during these conversions is needed before proposing them as industrial biocatalysts.

In this work, a comprehensive study on different parameters that could affect the performance of Methylovorus HMFO in the production of FDCA from HMF has been carried out for HMFO WT and its V367R, W466F, V367R/W466F and 8BxHMFO variants. Thus, the effect of pH on enzyme stability and activity, the inhibition by reaction product and by-product, the initial substrate concentration, the cofactor dependency, and the oxygen reactivity have been evaluated. This allowed to optimize the operational conditions for each enzyme variant, and to bring closer the application of the most relevant candidates for the enzymatic production of FDCA at an industrial scale. The information obtained will provide useful insights for future studies with HMFO-type enzymes, and will also contribute to the development of new HMFO variants for enhanced FDCA production from HMF.

Results and discussion

Effect of pH on FDCA production

First, the pH stability of the enzymes was analyzed by measuring their residual activity (on the standard substrate vanillyl alcohol) after 72 h of incubation in the range of pH 6.5–9.0 (Fig. 2a) since it has been reported that the Methylovorus enzyme and other HMFOs totally lost their activity after 24 h out of this range [24]. HMFO WT and 8BxHMFO remained stable in the full pH range, keeping 70–80% of their initial activity. V367R retained ~ 80% of its activity between pH 6.5 and 8.0, and ~ 40% at pH 9.0. Similar behaviors were observed for the W466F and V367R/W466F variants, as both remained more active at pH 7.5–8.0, but they lost most of the activity at pH 9.0. The V367R/W466F variant showed to be particularly unstable, as it lost > 50% of its activity at all the pH values tested.

Fig. 2
figure2

Effect of pH (a) and H2O2 (b) on HMFO stability, and influence of pH on FDCA production from HMF (c) and FFCA (d). a pH stability as shown by residual activities after 72-h incubation of the enzymes in 100 mM B&R buffer (pH 6.5–9) at 25 °C. b H2O2 stability as shown by residual activities after 72-h incubation of the enzymes with increasing amounts of H2O2 (0–30 mM) in 50 mM Tris/HCl, pH 7.5. The residual activities were measured with vanillyl alcohol as substrate. Percentages of FDCA (referred to initial substrate concentration) in c and d are shown after 24-h reaction of HMF or FFCA, respectively, with the HMFO WT and variants (4-h reaction with 8BxHMFO) at different pH values. The reactions were performed at 28 °C and 180 rpm shaking, using 1.5 mM substrate, and 2.5 µM enzyme, in 50 mM NaPi (pH 6.5) or Tris/HCl (pH 7.5, 8.0 and 9.0). Mean and standard deviation values from triplicate experiments are shown

A high dependence on pH has been recently reported for FDCA production by a WT HMFO [24]. Thus, this possible effect was evaluated here for the different variants. With this purpose, 24-h enzymatic reactions were performed at 28 °C in 50 mM NaPi, pH 6.5, or in 50 mM Tris/HCl, pH 7.5–9.0, and the production of FDCA from 1.5 mM HMF or FFCA was analyzed by high-performance liquid chromatography (HPLC) after 24 h (Fig. 2c and d, respectively). For the 8BxHMFO variant, yields after 4-h reaction were considered, since at 24 h total conversion was observed at all the pH values. For HMFO WT the optimal pH for FDCA production was 6.5. Surprisingly, all HMFO variants shifted this optimum to pH 8.0–9.0 for the oxidation of both substrates. The pH values in which the maximal half-lives were observed during HMF and FFCA conversion (Table 1) coincided with the pH at which each enzyme achieved the highest FDCA yields in 24-h reactions (Fig. 2c and d).

Table 1 Half-lives (h) of HMFO WT and variants (2.5 µM) during FDCA production from HMF and FFCA (1.5 mM) in 48-h reactions, at different pH values

Effect of H2O2 byproduct on FDCA production

In the oxidation of HMF to FDCA, three equivalents of H2O2 are produced by HMFO since the reaction takes place through two furfural intermediates (Fig. 1). Thus, another aspect to be considered is how this H2O2 would affect the enzyme stability or the reaction itself.

To study if the H2O2 accumulated during the reaction had some negative effect in enzyme stability, HMFO WT and its variants were incubated for 72 h with 0–30 mM H2O2 in Tris/HCl, pH 7.5, at 25 °C, and their residual activities were measured with vanillyl alcohol (Fig. 2b). All the enzymes were affected by H2O2 with the W466F and V367R/W466F variants retaining < 20% of the initial activity at all the H2O2 concentrations assayed. In contrast, the 8BxHMFO multiple variant kept at least ~ 50% of its activity in the whole H2O2 range, while the activity of the HMFO WT and V367R variant was always below 50% at H2O2 concentrations higher than 3 mM.

To discard an additional inhibitory effect of H2O2 on the FFCA oxidation reaction, as reported for AAO [25], FDCA production from FFCA by HMFO WT was evaluated along 48 h in the presence of 1.5–18 mM H2O2 (Additional file 1: Fig. S1). However, no strong differences were observed compared with the FDCA produced in absence of external H2O2. The H2O2 generated during catalysis was removed by the addition of catalase to increase the stability of the enzymes. The effect of catalase was milder at low substrate concentrations (~ 1.5 mM) but it was more relevant at higher HMF concentrations, as described below.

The H2O2 produced by HMFO along the reaction with FFCA was determined with the AmplexRed®/horseradish peroxidase (HRP) coupled assay, and compared with the amount of FDCA quantified by HPLC (Fig. 3). The results showed stoichiometric amounts of FDCA and H2O2 along the reaction, indicating that the oxidation of FFCA by HMFO takes place with H2O2 release. This contrast with the slower catalysis by AAO that, given the lack of H2O2 formation, was proposed to occur through a monooxygenase-type mechanism [25]. The difference makes the oxidation of FFCA by HMFO more efficient than by AAO, which requires much longer reaction times.

Fig. 3
figure3

Comparison of H2O2 and FDCA production during FFCA oxidation by HMFO. Reactions were performed at 28 °C in 50 mM Tris/HCl, pH 7.5, between FFCA (1.5 mM) and HMFO WT (2.5 µM). The products, FDCA and H2O2, were quantified after separation of the reaction mixture by HPLC and with AmplexRed/HRP assay, respectively. Mean and standard deviation values are shown

Effect of FFCA intermediate on FDCA production

Although HMFO is capable to carry out HMF oxidation to FDCA, its lower activity towards FFCA limits the efficiency of the whole reaction [23, 24]. To displace the reaction towards product formation we evaluated the effect that increasing amounts of HMF or FFCA had on FDCA production by HMFO WT (Fig. 4a and b, respectively). At the highest substrate concentrations assayed (15 mM) the FDCA yields from HMF decreased drastically. The fact that similar inhibition was observed with increasing amounts of FFCA suggests that the reaction is inhibited by this reaction intermediate. In the presence of catalase, the same inhibition profiles were observed upon increasing substrate concentration, although higher FDCA yields were attained, being the highest with 6 mM HMF (Fig. 4a).

Fig. 4
figure4

FDCA production from different HMF (a) and FFCA (b) concentrations and catalase effect. FDCA production by HMFO WT (2.5 µM) from increasing HMF (left) and FFCA (right) concentrations (1.5–15 mM) is shown in the absence and presence of catalase. Reactions (48 h) were performed in 50 mM Tris/HCl, pH 7.5, at 28 °C. Mean and standard deviation values are shown

The steady-state kinetics for HMF and DFF oxidations were measured with AmplexRed®/HRP in a continuous assay. The saturation profiles for all the variants discarded any inhibitory effect by these two substrates (Additional file 1: Fig. S2 and Table S1). However, an end-point method was required to analyze the kinetics for FFCA oxidation, given the much lower activities on this substrate. Since important differences in FDCA yields from FFCA were observed depending on pH, these kinetic measurements were performed at pH values from 6.0 to 9.0, and an excess of catalase was added to ensure the enzyme stability. Reactions were stopped after 48 h for HMFO WT and after 30 min for the improved HMFO variants, and the FDCA formed was quantified by HPLC (Fig. 5). Both HMFO WT and variants showed a strong inhibition by FFCA that, surprisingly, was highly dependent on pH. To better understand this inhibition, residual activity of HMFO WT was measured (with vanillyl alcohol) when FFCA was added (time 0 h) and before stopping the reaction after 48 h, at the different substrate concentrations used in the kinetic curves (Additional file 1: Fig. S3a and b). The results indicate that at those FFCA concentrations where inhibition was detected, the enzymatic activity was lost from the moment that enzyme and FFCA were put together. To know if this inhibition could be reverted, enzymes were dialyzed in 50 mM Tris/HCl overnight, pH 7.5, after their incubation with 15 mM FFCA for 5 min. However, all of them remained inactive (data not shown) indicating irreversible inhibition by FFCA. These data suggest that FFCA would bind at the active site or in its access channel preventing the enzyme to act in successive catalytic cycles.

Fig. 5
figure5

Effect of pH on kinetic curves of FFCA oxidation by HMFO WT and variants. Reaction rates (v/[Ez] as µmol of product per µmol of enzyme per time, in min−1) were obtained for end-point reactions of HMFO WT, and its V367R, W466F, V367R/W466F and 8BxHMFO variants with increasing amounts of FFCA, in 50 mM NaPi (pH 6.0–6.5) or Tris/HCl (pH 7.0–9.0) at 25 °C, in the presence of catalase. FDCA production was quantified in 48-h and 30-min reactions for the HMFO WT and variants, respectively

Due to the high inhibition observed at different pH values (Fig. 5), only apparent kinetic constants for FFCA could be calculated for each enzyme and pH (Table 2). Catalytic efficiencies were the highest at pH 6.0 for HMFO WT and in the range of pH 7.0–8.0 for the different variants. For all the enzymes, inhibition occurred at higher substrate concentrations when kinetics were performed at more basic pH. Moreover, 8BxHMFO showed better catalytic efficiencies than V367R/W466F and the other variants at any pH tested. This pH-dependent inhibition by FFCA is in agreement with the efficiencies observed at the different pH values in long-term HMF and FFCA reactions (Fig. 2c and d), being the optimal pH for these conversions those in which the enzymes present less FFCA inhibition (within the pH range in which the highest apparent efficiencies are observed).

Table 2 Apparent catalytic efficiencies (kcat/Km, mM−1 min−1) for FFCA oxidation by HMFO WT and variants, at different pH values

Effect of O2 concentration on FDCA production

The high enzyme inhibition by FFCA prevented evaluation of the reaction under saturating HMF concentrations. However, we were able to evaluate the effect of oxygen saturation (the second substrate required by the oxidase) on FDCA production by HMFO WT and its variants. With this purpose, the enzymes were mixed with 6 mM HMF and catalase excess at 28 °C, bubbled with O2, corresponding to 1.22 mM concentration [33], and the FDCA yields were compared with those obtained using atmospheric O2, corresponding to 0.25 mM concentration, after 48-h reaction (Additional file 1: Fig S4a). Although in the case of HMFO WT some improvement was observed at higher O2 concentration, for the HMFO variants, which are more efficient for FFCA oxidation, similar results were obtained under both conditions. This suggests that the current reactions would be already saturated under atmospheric O2. Nevertheless, additional improvements enabling use of higher substrate concentrations, an important point for scaling up the process, could be obtained by increasing the O2 diffusion into the reaction medium. In this sense, continuous-flow microreactor technology has been reported as a safe and scalable way to approach oxidation reactions [34, 35] and different reactor designs—such as simple flow reactors, tube-in-tube reactors, agitated tube reactors and continuous agitated cell reactors—have been used for O2-dependent enzymes showing higher oxygen transfer rates than in batch reactions [36,37,38,39,40].

Effect of FAD addition on FDCA production

It has been suggested that higher FDCA yields can be attained by adding FAD to HMFO WT reactions [23] to prevent eventual inactivation of the enzyme by cofactor dissociation. Although such effect was claimed based on 95% FDCA yield in 24-h reactions of 4 mM HMF (and 20 µM HMFO) in presence of 20 µM FAD, the study lacked the FAD-less controls (with 4 mM HMF and 20 μM HMFO) to demonstrate such effect. Therefore, to confirm/discard a positive effect of FAD, HMF (6 mM) reactions with and without 20 μM FAD, in pH 6.5 50 mM NaPi for HMFO WT and pH 8.0 Tris/HCl for the variants, were performed here. The FDCA yields and residual activities of the enzymes (enabling half-life, t1/2, calculation) were followed along 48 h (Table 3 and Additional file 1: Fig. S4b). No differences were observed for HMFO WT and V367R, while a slight increase was observed when FAD was added to variants bearing the W166F mutation (~ 1.1-fold for 8BxHMFO and 1.5 fold for W466F and V367R/W466F). Since the efficiency for FFCA oxidation was similar in absence and presence of FAD (Additional file 1: Table S2) the slight effect of the cofactor can be attributed to higher stability of these variants when FAD was added to the reaction (with half-lives 1.2–1.5-folds higher than in absence of the cofactor). These results make sense for variants containing a mutation at W466, since this residue is close to the flavin ring, and its removal affect protein stability [31].

Table 3 Effect of FAD or/and catalase on catalytic performance parameters—FDCA concentration (mM) and yield (%), enzyme half-life (t1/2), and total turnover number (TTN)—for the production of FDCA from HMF (6 mM) by the HMFO WT and variants

Anyway, it is necessary to remark that the effect of FAD is much lower than the effect of adding catalase to the reaction (Table 3 and Additional file 1: Fig. S4b). The removal of H2O2 by catalase positively affects both stabilities and FDCA yields for all the enzymes. An improvement of 1.5–3-folds was observed for most of the variants and up to 9-folds for W466F, while the half-lives significantly increased for HMFO WT and the V367R and 8BxHMFO variants. In these conditions, variants V367R and 8BxHMFO achieved full conversion of 6 mM HMF into FDCA after 48 h of reaction. Moreover, although the addition of catalase plus FAD increased the half-life of all the enzymes, the FDCA yield was only increased for HMFO WT (while FDCA production by its variants was similar to that observed upon the only addition of catalase). Finally, it was confirmed that only traces of HMFCA (< 1%) were produced in HMF controls with and without catalase or FAD in the absence of enzyme, excluding any activity of catalase or FAD oxidizing these furfurals (Additional file 1: Fig. S5).

Optimized conditions for FDCA production

Taking all the above results together, the conditions for FDCA production with the HMFO enzymes were optimized. Among the variants analyzed, V367R and 8BxHMFO were selected as the most suitable for the scalability of the process, since they exhibit higher stability and better performance. Reactions were carried out at pH 8.0 (in 50 mM Tris/HCl) since this is the optimal pH for FDCA production by these variants (Fig. 2). The stability of the enzymes during the reactions was ensured by addition of a catalase excess, as shown by their higher half-life under these conditions (Table 3). The addition of FAD was excluded since the benefit is not relevant, as shown above, and the high cost of the cofactor limits its use for an industrial application.

Considering the relatively low substrate concentration used in the previous experiments, we explored increasing HMF concentrations (up to 12 mM, since accumulation of higher concentrations of FFCA results in enzyme inhibition, Fig. 5). However, the final amounts of FDCA product were barely improved, reaching < 7.5 mM of FDCA after 6 days of reaction, despite of the use of higher HMF concentration (Additional file 1: Fig. S6a). Moreover, under these conditions, the stability of the enzymes decreased drastically over time (Table 4 and Additional file 1: Fig. S6b).

Table 4 Catalytic performance parameters—FDCA concentration (mM) and yield (%), residual activity, and total turnover number (TTN)—for the production of FDCA from 6–12 mM HMF (including 6 mM re-dosage after 6 mM initial concentration) by the V367R and 8BxHMFO variants

Therefore, taking advantage of the high residual activity of V367R and 8BxHMFO at the end of reactions with 6 mM HMF, we decided to supplement the reactions with additional 6 mM HMF and catalase excess when the first conversion was completed after 2 days (Fig. 6a). In this way, almost 10 mM FDCA was attained in 6 days reaching total turnover numbers (TTN) over 11,000 (Table 4). As FFCA accumulation under these conditions could result in enzyme inactivation limiting final product concentration, lower enzyme doses (1.25 µM) were assayed (Fig. 6b). Under these conditions, slower production and minor accumulation of FFCA was expected, resulting in more active enzyme being able to complete the conversion till FDCA. With this amount of enzyme, a second addition of substrate and catalase was applied after 4 days of reaction, when no more conversion was observed. In this way, almost 12 mM FDCA was obtained after 12 days, before enzyme inactivation, and TTN values of 26,000 and 27,000 were reached for the 8BxHMFO and V367R variants, respectively (Table 4). Therefore, taking advantage from the high stability of both variants under optimized conditions, we were able to double the FDCA yields obtained by re-dosing substrate to overcome the inhibition by the intermediate FFCA. By applying these reaction conditions, FDCA yields ≥ 90% are attained facilitating downstream procedures to obtain pure FDCA. However, further reaction upscaling is necessary for more realistic evaluation of product purification under industrially-relevant conditions.

Fig. 6
figure6

Optimized HMF conversion using two different V367R and 8BxHMFO doses. a Reactions with 2.5 µM enzyme, and HMF/catalase re-dosage after 2 days. b Higher FDCA production by lowering the enzyme dose (to 1.25 µM), and HMF/catalase re-dosage after 4 days. FDCA yields (lines) and residual enzyme activities (dashes) are shown during HMF (6 mM concentration, plus 6 mM addition after 2 or 4 days) reactions with the V367R (black) and 8BxHMFO (red) variants, in 50 mM Tris/HCl, pH 8.0, in the presence of catalase. FDCA production was quantified by HPLC, and residual activities were measured with vanillyl alcohol, in 50 mM Tris/HCl, pH 7.5. Mean and standard deviation values from triplicate experiments are shown

Conclusions

Biocatalysts for industrial processes must fulfill specific features to ensure the feasibility and applicability of the resulting bioprocess. Aspects such as enzyme stability, cofactor requirement, reaction conditions and substrate range have to be optimized for industrial application [41]. Here, we have identified several limitations of HMFO that can prevent an efficient production of FDCA from HMF, such as the low stability of the enzyme under high concentrations of H2O2, and its strong inhibition by the FFCA intermediate. However, the above limitations in the enzymatic production of FDCA from HMF can be overcome with the addition of catalase to the reaction mixture and controlling the dose of substrate, respectively. Other aspects such as O2 diffusion into the reaction medium are also important for a further optimization of these processes. The above findings should be taken into account for the use of HMFO variants in an industrial context. They will also pave the way for the characterization of other HMFOs as well as in the development of new variants that enable a more efficient production of FDCA from HMF.

Materials and methods

Chemicals

HMF was kindly provided by AVA Biochem. DFF, FDCA, FAD, catalase, HRP, vanillyl alcohol was purchased from Sigma-Aldrich (St. Louis, MO, USA). FFCA was purchased from TCI America (Portland, OR, USA). AmplexRed® was obtained from Invitrogen (Walthem, MA, USA).

Genes, plasmid and site-directed mutagenesis

The gene encoding HMFO from Methylovorus sp MP688 (NCBI accession number WP_013440946) was synthesized by ATG biosynthetic (Merzhausen, Germany) and then subcloned into the pET23b(+) plasmid (Novagen). Simple variants of HMFO were performed by whole plasmid PCR using the pET23b-HMFO plasmid as a template. Forward and reverse primers were designed complementary to opposite strands of the DNA region containing the desired mutation. The sequence of the forward synthetic primers (substituted nucleotides are in bold and the triplet containing the mutation is underlined) were 5'-GCA AGC GCT CGT TTC TGG GTG AAC AAG C-3' for V367R and 5'-C GTC GGC GGT GTT TTT CAT GCG AG-3' for W466F. For V367R/W466F, W466F primers were employed using variant V367R as template. Template DNA was cleaved with DpnI (Roche). E. coli DH5α cells were transformed with the plasmids through thermal shock. Plasmid purification from E. coli DH5α cultures in LB-ampicillin 100 µg/mL was carried out using High Pure Plasmid Isolation Kit (Roche). The octuple HMFO variant (8BxHMFO) containing mutations I73V, H74Y, G356K, V367R, T414K, A419Y, A435E and W466F was synthesized by ATG biosynthetic (Merzhausen, Germany) and subcloned into the pET23b(+) plasmid (Novagen). Introduction of mutations was confirmed by sequencing.

Enzyme production and purification of HMFOs

For recombinant protein expression, the constructed plasmids were transformed into E. coli BL21(DE3)pLysS cells. Overnight cultured cells were diluted 1:30 in 1 L of LB medium containing 100 µg/mL ampicillin and 34 µg/mL chloramphenicol, and grown at 37 °C and 200 rpm until an OD500nm of 1.0 was reached. Cells were induced with 0.1 mM isopropyl β-d-1-thiogalactopyranoside for 72 h at 16 °C and 150 rpm. Cells were harvested by centrifugation at 7000 rpm for 5 min at 4 °C and frozen for the expression of lysozyme. Bacterial pellets were resuspended in lysis buffer (50 mM Tris/HCl, pH 8.0, supplemented with 10 mM EDTA and 5 mM dithiothreitol) and treated with 0.1 mg/mL of DNase (Roche) at 4 °C for 30 min. The cell extracts were obtained after cell disruption through sonication (10 cycles of 1 min at 4 °C), centrifugation at 13,000 rpm and 4 °C for 30 min, and ultracentrifugation of supernatant at 30,000 rpm and 4 °C for 1 h to eliminate insoluble debris. The soluble fraction obtained was preserved at − 20 °C until its purification.

Native HMFO and variants were purified following the same protocol previously described for HMFO WT [24]. Two consecutive anionic-exchange chromatographic steps, first with a Resource Q 6-mL (GE Healthcare) column and then with Mono Q 5/50 GL 1-mL column were used to obtain pure fractions of the enzymes. The purification process was followed by analyzing each fraction in a SDS-PAGE 12% (v/v) polyacrylamide separation gel (Additional file 1: Fig. S7).

Spectral properties of HMFOs

The UV–visible spectra of the purified proteins were recorded between 250 and 700 nm in a Cary4000 spectrophotometer. The spectra of the folded enzymes and the free flavin, obtained by heat treatment of the enzyme (95 °C for 5 min) and centrifugation for 45 min, were recorded to calculate the extinction coefficient at the band-I of the flavin, using the known extinction constant for FAD (ε450nm = 11,300 mM−1 cm−1) [42] (Additional file 1: Table S3). The calculated extinction coefficient of each variant was used to estimate the protein concentrations.

pH and H2O2 stability of native HMFO and variants

pH stability was estimated by incubating the purified enzymes at different pH (6–9) in Britton-Robinson buffer. To determine stability to H2O2, purified enzymes were incubated in the presence of 0 to 30 mM H2O2 in 50 mM Tris/HCl, pH 7.5. Samples were incubated at 25 °C and residual activities were measured at 0, 24, 48 and 72 h by oxidation of 3 mM vanillyl alcohol in 50 mM Tris/HCl, pH 7.5, at 25 °C. For each enzyme, the highest activity obtained at the different times and pH or H2O2 conditions was taken as 100%, and the percentages of residual activity of the remaining measures were referred to this value.

FDCA production by HMFOs

Effect of pH on HMF and FFCA oxidation was determined by analyzing FDCA yields after incubating each enzyme (2.5 µM) with HMF or FFCA (1.5 mM) in 50 mM NaPi, pH 6.5, and in 50 mM Tris/HCl, pH 7.5, 8.0 and 9.0. Effect of H2O2 on FDCA production was analyzed by incubating HMFO WT (2.5 µM) with HMF (1.5 mM) in presence of different concentrations of H2O2. FDCA:H2O2 stoichiometry was evaluated by quantifying FDCA by HPLC (see below) and H2O2 using AmplexRed®/HRP. Effect of oxygen was studied by analyzing FDCA yields after incubation of the enzymes (2.5 µM) with HMF (6 mM) and catalase excess (10–25 U/mL) and bubbling the reactions with 1.22 mM of O2. Effect of cofactor addition was assayed by incubating the enzymes (2.5 µM) with 6 mM HMF (6 mM) with and without the addition of FAD (20 μM).

All reactions (unless indicated) were performed in 50 mM NaPi, pH 6.5, for HMFO WT and 50 mM Tris/HCl, pH 8.0, for HMFO variants, at 28 °C under continuous shaking (180 rpm). In all cases, solutions were treated in the same conditions but in the absence of enzyme as negative controls.

Residual activity of HMFOs along the reactions was measured just after taking aliquots at different times (usually 0, 4, 24 and 48 h or every 24 h in longer reactions), before addition of HCl, by monitoring their activity against vanillyl alcohol. The activity decay as a function of time was calculated from Eq. 1 allowing the estimation of the half-life (Eq. 2):

$$HMFOactivity\; \left( \% \right) = HMFO act_{0} \, \cdot e^{ - \lambda t}$$
(1)
$$t_{1/2} = \frac{ln\left( 2 \right)}{\lambda }$$
(2)

where λ is the activity decay constant, and t1/2 is the enzyme half-life.

Product identification

After substrate conversion, 150 µL aliquots were taken at different times (usually 0, 4, 24 and 48 h or every 24 h in longer reactions) and reactions were stopped by adding 1 M HCl up to pH 2–3. Furfural oxidation was analyzed by HPLC using an ion-exchange SUPELCOGEL C-610H column (300 × 7.8 mm, 9 µm particle size, SUPELCO). Compounds were eluted using 5 mM H2SO4 as mobile phase at a flow rate of 0.6 mL/min at 30 °C and detection was done at 264 nm. The retention times of FDCA, HMFCA, FFCA, HMF and DFF were 21, 27, 30, 42 and 52 min, respectively (Additional file 1: Fig. S8). Calibration curves were made with 0.05, 0.1, 0.2, 0.4, 0.75 and 1.5 mM solutions of each component that might be present during the reaction. H2O2 quantification was performed using a peroxidase coupled assay before the addition of HCl. In this assay, HRP (6 U/mL final concentration) reacts with AmplexRed® reagent (75 ng/mL final concentration) in presence of H2O2 producing a pink product (resorufin; ε563nm = 52,000 M−1 cm−1). Quantification was performed using a calibration curve with known concentrations of H2O2. The standard deviations were always ≤ 5% of the mean values obtained.

Kinetic analysis

Steady-state kinetic parameters for HMF and DFF oxidation by HMFOs were calculated by monitoring the production of H2O2 during oxidation of the different substrates using a HRP-coupled assay with AmplexRed® as final substrate in 50 mM Tris/HCl, pH 7.0, as previously described [24]. The oxidation of FFCA was measured in end-time mode by incubating different concentrations of FFCA (0.4–25 mM) with the enzymes (0.3–1.5 µM, depending on the enzyme) supplemented with catalase excess (10–25 U/mL) at 25 °C in 50 mM NaPi, pH 6.0–6.5, or 50 mM Tris/HCl, pH 7.0–9.0, under continuous shaking. Reactions were stopped after 48 h for WT HMFO or at 30 min for HMFO variants, and the products were quantified by HPLC as described above. The rate of FDCA or H2O2 formation (v/[Ez]) was estimated as the product formed (µmol) per enzyme concentration (µmol) per time of reaction (resulting in min−1 units).

In all cases, kinetic parameters were determined by fitting the initial reaction rates at different alcohol or aldehyde concentrations to the Michaelis–Menten equation (Eq. 3) using Origin software.

$$\frac{{v_{0} }}{\left[ E \right]} = \frac{{k_{cat} \left[ S \right]}}{{K_{m} + \left[ S \right]}}$$
(3)

where kcat is the catalytic constant, and Km is the Michaelis–Menten constant.

When apparent kinetic parameters could not be estimated, the linear relation between the rates (min−1) and the substrate concentration (mM) was used as a measure of catalytic efficiency (kobs/[FFCA]).

Availability of data and materials

All the data supporting the conclusions of this article are included within the article and its supporting information. Additional information can be provided by the corresponding authors under request.

Abbreviations

AAO:

Aryl-alcohol oxidase

FDCA:

2,5-Furandicarboxylic acid

FFCA:

5-Formylfurancarboxylic acid

GMC:

Glucose-methanol-choline oxidase/dehydrogenase (enzyme superfamily)

HMF:

5-Hydroxymethylfurfural

HMFCA:

5-Hydroxymethylfurancarboxylic acid

HMFO:

HMF oxidase

HPLC:

High-performance liquid chromatography

HRP:

Horseradish peroxidase

k cat :

Catalytic constant

k cat/K m :

Catalytic efficiency

K m :

Michaelis constant

PEF:

Poly(ethylene-2,5-furandicarboxylate)

PET:

Poly(ethylene-terephthalate)

TTN:

Total turnover number

References

  1. 1.

    Geyer R, Jambeck JR, Law KL. Production, use, and fate of all plastics ever made. Sci Adv. 2017;3:e1700782.

    Article  Google Scholar 

  2. 2.

    Gallezot P. Conversion of biomass to selected chemical products. Chem Soc Rev. 2012;41:1538–58.

    CAS  Article  Google Scholar 

  3. 3.

    Hwang KR, Jeon W, Lee SY, Kim MS, Park YK. Sustainable bioplastics: Recent progress in the production of bio-building blocks for the bio-based next-generation polymer PEF. Chem Eng J. 2020;390:124636.

    CAS  Article  Google Scholar 

  4. 4.

    Loos K, Zhang R, Pereira IS, Agostinho B, Hu H, Maniar D, Sbirrazzuoli N, Silvestre AJD, Guigo N, Sousa AF. A perspective on PEF synthesis, properties, and end-life. Front Chem. 2020;8:585.

    CAS  Article  Google Scholar 

  5. 5.

    Papageorgiou GZ, Tsanaktsis V, Bikiaris DN. Synthesis of poly(ethylene furandicarboxylate) polyester using monomers derived from renewable resources: thermal behavior comparison with PET and PEN. Phys Chem Chem Phys. 2014;16:7946–58.

    CAS  Article  Google Scholar 

  6. 6.

    Burgess SK, Leisen JE, Kraftschik BE, Mubarak CR, Kriegel RM, Koros WJ. Chain mobility, thermal, and mechanical properties of poly(ethylene furanoate) compared to poly(ethylene terephthalate). Macromolecules. 2014;47:1383–91.

    CAS  Article  Google Scholar 

  7. 7.

    Rajesh RO, Pandey A, Binod P. Bioprocesses for the production of 2,5-furandicarboxylic acid. In: Varjani S, Binod P, Kumar S, Khare SK, editors. Biosynthetic technology and environmental challenges. Berlin: Springer; 2018.

    Google Scholar 

  8. 8.

    Yuan H, Liu H, Du J, Liu K, Wang T, Liu L. Biocatalytic production of 2,5-furandicarboxylic acid: recent advances and future perspectives. Appl Microbiol Biotechnol. 2020;104:527–43.

    CAS  Article  Google Scholar 

  9. 9.

    Hu I, He AY, Liu XY, Xia J, Xu JX, Zhou SY, Xu JM. Biocatalytic transformation of 5-hydroxymethylfurfural into high-value derivatives: recent advances and future aspects. ACS Sustain Chem Eng. 2018;6:15915–35.

    CAS  Article  Google Scholar 

  10. 10.

    Saikia K, Rathankumar AK, Kumar PS, Varjani S, Nizar M, Lenin R, George J, Vaidyanathan VK. Recent advances in biotransformation of 5-hydroxymethylfurfural: challenges and future aspects. J Chem Technol Biotechnol. 2021. https://doi.org/10.1002/jctb.6670.

    Article  Google Scholar 

  11. 11.

    Sajid M, Zhao X, Liu D. Production of 2,5-furandicarboxylic acid (FDCA) from 5-hydroxymethylfurfural (HMF): recent progress focusing on the chemical-catalytic routes. Green Chem. 2018;20:5427–53.

    CAS  Article  Google Scholar 

  12. 12.

    Zhao D, Su T, Wang Y, Varma RS, Len C. Recent advances in catalytic oxidation of 5-hydroxymethylfurfural. Mol Catal. 2020;495:111133.

    CAS  Article  Google Scholar 

  13. 13.

    Domínguez de María P, Guajardo N. Biocatalytic valorization of furans: opportunities for inherently unstable substrates. Chemsuschem. 2017;10:4123–34.

    Article  Google Scholar 

  14. 14.

    Troiano D, Orsat V, Dumont MJ. Status of biocatalysis in the production of 2,5-furandicarboxylic acid. ACS Catal. 2020;10:9145–69.

    CAS  Article  Google Scholar 

  15. 15.

    Lalanne L, Nyanhongo GS, Guebitz GM, Pellis A. Biotechnological production and high potential of furan-based renewable monomers and polymers. Biotechnol Adv. 2021;48:107707.

    CAS  Article  Google Scholar 

  16. 16.

    Carro J, Ferreira P, Rodríguez L, Prieto A, Serrano A, Balcells B, Ardá A, Jiménez-Barbero J, Gutiérrez A, Ullrich R, Hofrichter M, Martínez AT. 5-Hydroxymethylfurfural conversion by fungal aryl-alcohol oxidase and unspecific peroxygenase. FEBS J. 2015;282:3218–29.

    CAS  Article  Google Scholar 

  17. 17.

    Karich A, Kleeberg BS, Ullrich R, Hofrichter M. Enzymatic preparation of 2,5-furandicarboxylic acid (FDCA)—a substitute of terephthalic acid-by the joined action of three fungal enzymes. Microorganisms. 2018;6:5.

    CAS  Article  Google Scholar 

  18. 18.

    McKenna SM, Leimkuhler S, Herter S, Turner NJ, Carnell AJ. Enzyme cascade reactions: synthesis of furandicarboxylic acid (FDCA) and carboxylic acids using oxidases in tandem. Green Chem. 2015;17:3271–5.

    CAS  Article  Google Scholar 

  19. 19.

    Wu S, Liu Q, Tan H, Zhang F, Yin H. A novel 2,5-furandicarboxylic acid biosynthesis route from biomass-derived 5-hydroxymethylfurfural based on the consecutive enzyme reactions. Appl Biochem Biotechnol. 2020;191:1470–82.

    CAS  Article  Google Scholar 

  20. 20.

    Qin YZ, Li YM, Zong MH, Wu H, Li N. Enzyme-catalyzed selective oxidation of 5-hydroxymethylfurfural (HMF) and separation of HMF and 2,5-diformylfuran using deep eutectic solvents. Green Chem. 2015;17:3718–22.

    CAS  Article  Google Scholar 

  21. 21.

    McKenna SM, Mines P, Law P, Kovacs-Schreiner K, Birmingham WR, Turner NJ, Leimkühler S, Carnell AJ. The continuous oxidation of HMF to FDCA and the immobilisation and stabilisation of periplasmic aldehyde oxidase (PaoABC). Green Chem. 2017;19:4660–5.

    CAS  Article  Google Scholar 

  22. 22.

    Jia HY, Zong MH, Zheng GW, Li N. One-pot enzyme cascade for controlled synthesis of furancarboxylic acids from 5-hydroxymethylfurfural by H2O2 internal recycling. Chemsuschem. 2019;12:4764–8.

    CAS  Article  Google Scholar 

  23. 23.

    Dijkman WP, Groothuis DE, Fraaije MW. Enzyme-catalyzed oxidation of 5-hydroxymethylfurfural to furan-2,5-dicarboxylic acid. Angew Chem. 2014;126:6633–6.

    Article  Google Scholar 

  24. 24.

    Viñambres M, Espada M, Martínez AT, Serrano A. Screening and evaluation of new hydroxymethylfurfural oxidases for furandicarboxylic acid production. Appl Environ Microbiol. 2020;86:00842–920.

    Article  Google Scholar 

  25. 25.

    Serrano A, Calviño E, Carro J, Sánchez-Ruiz MI, Cañada FJ, Martínez AT. Complete oxidation of hydroxymethylfurfural to furandicarboxylic acid by aryl-alcohol oxidase. Biotechnol Biofuels. 2019;12:217.

    Article  Google Scholar 

  26. 26.

    Cavener DR. GMC oxidoreductases. A newly defined family of homologous proteins with diverse catalytic activities. J Mol Biol. 1992;223:811–4.

    CAS  Article  Google Scholar 

  27. 27.

    Dijkman WP, Fraaije MW. Discovery and characterization of a 5-hydroxymethylfurfural oxidase from Methylovorus sp strain MP688. Appl Environ Microbiol. 2014;80:1082–90.

    Article  Google Scholar 

  28. 28.

    Ruiz-Dueñas FJ, Ferreira P, Martínez MJ, Martínez AT. In vitro activation, purification, and characterization of Escherichia coli expressed aryl-alcohol oxidase, a unique H2O2-producing enzyme. Protein Express Purif. 2006;45:191–9.

    Article  Google Scholar 

  29. 29.

    Jankowski N, Koschorreck K, Urlacher VB. High-level expression of aryl-alcohol oxidase 2 from Pleurotus eryngii in Pichia pastoris for production of fragrances and bioactive precursors. Appl Microbiol Biotechnol. 2020;104:9205–18.

    CAS  Article  Google Scholar 

  30. 30.

    Román R, Loncar N, Casablancas A, Fraaije MW, Gonzalez G. High-level production of industrially relevant oxidases by a two-stage fed-batch approach: overcoming catabolite repression in arabinose-inducible Escherichia coli systems. Appl Microbiol Biotechnol. 2020;104:5337–45.

    Article  Google Scholar 

  31. 31.

    Dijkman WP, Binda C, Fraaije MW, Mattevi A. Structure-based enzyme tailoring of 5-hydroxymethylfurfural oxidase. ACS Catal. 2015;5:1833–9.

    CAS  Article  Google Scholar 

  32. 32.

    Martin C, Ovalle Maqueo A, Wijma HJ, Fraaije MW. Creating a more robust 5-hydroxymethylfurfural oxidase by combining computational predictions with a novel effective library design. Biotechnol Biofuels. 2018;11:56.

    Article  Google Scholar 

  33. 33.

    Rounds SA, Wilde FD, Ritz GF: Dissolved oxygen (ver. 3.0).U.S. Geological Survey Techniques of WaterResources Investigations, book 9, chap. A6, sec. 6.2. 2013. https://doi.org/10.3133/tm9A6.2.

  34. 34.

    Gemoets HPL, Su Y, Shang M, Hessel V, Luque R, Noël T. Liquid phase oxidation chemistry in continuous-flow microreactors. Chem Soc Rev. 2016;45:83–117.

    CAS  Article  Google Scholar 

  35. 35.

    Tamborini L, Fernandes P, Paradisi F, Molinari F. Flow bioreactors as complementary tools for biocatalytic process intensification. Trends Biotechnol. 2018;36:73–88.

    CAS  Article  Google Scholar 

  36. 36.

    Gasparini G, Archer I, Jones E, Ashe R. Scaling up biocatalysis reactions in flow reactors. Org Process Res Dev. 2012;16:1013–6.

    CAS  Article  Google Scholar 

  37. 37.

    Jones E, McClean K, Housden S, Gasparini G, Archer I. Biocatalytic oxidase: batch to continuous. Chem Eng Res Des. 2012;90:726–31.

    CAS  Article  Google Scholar 

  38. 38.

    Ringborg RH, Pedersen AT, Woodley JM. Automated determination of oxygen-dependent enzyme kinetics in a tube-in-tube flow reactor. ChemCatChem. 2017;9:3285–8.

    CAS  Article  Google Scholar 

  39. 39.

    Pedersen AT, de Carvalho TM, Sutherland E, Rehn G, Ashe R, Woodley JM. Characterization of a continuous agitated cell reactor for oxygen dependent biocatalysis. Biotechnol Bioeng. 2017;114:1222–30.

    Article  Google Scholar 

  40. 40.

    van Schie MMCH, Pedroso de Almeida T, Laudadio G, Tieves F, Fernández-Fueyo E, Timothy N, Arends IWCE, Hollmann F. Biocatalytic synthesis of the Green Note trans-2-hexenal in a continuous-flow microreactor. Beilstein J Org Chem. 2018;14:697–703.

    Article  Google Scholar 

  41. 41.

    Schmid A, Dordick JS, Hauer B, Kiener A, Wubbolts M, Witholt B. Industrial biocatalysis today and tomorrow. Nature. 2001;409:258–68.

    CAS  Article  Google Scholar 

  42. 42.

    Macheroux P. UV-visible spectroscopy as a tool to study flavoproteins. In: Chapman SK, Reid GA, editors. Flavoprotein protocols. Totowa: Humana Press; 1999. p. 1–7.

    Google Scholar 

Download references

Acknowledgements

We acknowledge support of the publication fee by the CSIC Open Access Publication Support Initiative through its Unit of Information Resources for Research (URICI). AVA Biochem (Switzerland) is acknowledged for HMF supply.

Funding

This work has been funded by the H2020 BBI-JU (https://www.bbi-europe.eu) EnzOx2 (H2020-BBI-PPP-2015-2-720297; https://www.enzox2.eu) project, the GENOBIOREF (BIO2017-86559-R) project of the Spanish Ministry of Science & Innovation (co-financed by FEDER funds), the CSIC project PIE-201620E081, and the CSIC interdisciplinary platform for “Sustainable Plastics towards a Circular Economy” (SUSPLAST).

Author information

Affiliations

Authors

Contributions

MIS-R performed the experiments and wrote the first manuscript draft. AS designed and contributed to the experiments, and revised the results obtained. AS and ATM wrote the final version of the manuscript. All authors contributed to the discussion and conclusions obtained. All authors read and approved the final manuscript.

Corresponding authors

Correspondence to Angel T. Martínez or Ana Serrano.

Ethics declarations

Ethics approval and consent to participate

Not applicable.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Additional information

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Supplementary Information

Additional file 1: Table S1.

Steady-state kinetic parameters for HMF, DFF and FFCA oxidation. Table S2. Effect of FAD on FFCA oxidation. Table S3. Spectroscopic properties of the HMFO WT and variants. Fig. S1. Effect of H2O2 on FDCA production from FFCA. Fig. S2. Kinetic curves of HMF and DFF oxidation. Fig. S3 Effect of FFCA on HMFO kinetics and residual activity. Fig. S4. Effect of oxygen, FAD and catalase on FDCA production. Fig. S5. HMF control reactions without HMFO. Fig. S6. Reactions of HMFO variants with different HMF concentrations. Fig. S7. SDS-PAGE of purified HMFOs. Fig. S8. HPLC separation of HMF-derived furfurals.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Sánchez-Ruiz, M.I., Martínez, A.T. & Serrano, A. Optimizing operational parameters for the enzymatic production of furandicarboxylic acid building block. Microb Cell Fact 20, 180 (2021). https://doi.org/10.1186/s12934-021-01669-1

Download citation

Keywords

  • Enzymatic catalysis
  • Hydroxymethylfurfural oxidase
  • Catalase
  • Enzyme engineering
  • 2,5-Furandicarboxylic acid product
  • 5-Formylfurancarboxylic acid intermediate
  • Reaction pH
  • Hydrogen peroxide by-product
  • Enzyme inhibition
  • Reaction optimization