2.1. Suitability of IL-Lipase Combined Tools for the Esterification of FFAs with HT
The biocatalytic esterification of two substrates mutually immiscible, such as an aromatic alcohol, like HT, and an FFA as an acyl donor, may be considered the main handicap for a good performance, which is usually overcome by using chemical derivatives of substrates [
19] or a great excess of inert solvents [
20] to facilitate the reaction. By using ILs, many biocatalytic esterification reactions have been successfully carried out, where the easy recovery for reuse of this solvent was the main flag of greenness. As a representative example, the hexanoic acid (Hex) was selected as an acyl donor to carry out the biocatalytic esterification with HT by using a 1:4 HT:Hex molar ratio in the SLIL [C
12mim][NTf
2] as a green solvent. After the addition of the immobilized
C. antarctica lipase B Novozym 435 (N435) (400 mg/mmol HT), the mixture was incubated at 80
°C under magnetic stirring, where the presence of the MS 13X dehydrating agent allowed the reaction equilibrium to shift towards the synthetic side by withdrawing the released water by-product. Under these conditions, the hydroxytyrosyl hexanoate (HT-Hex) product was obtained at 87% yield after 3 h reaction time, as determined by HPLC (see
Table 1, entry 4). The synthesis of the product was also confirmed by ATR-FTIR, revealing the formation of an ester bond through the identification of the C=O stretching by the shift of the vibration band of the carboxyl group from 1704 cm
−1 to 1735 cm
−1 and the detection of a new band at 1238 cm
−1 corresponding to the C-O-C stretching (see
Figure S1). In the same context, the HT-Hex product was identified and characterized by HPLC-MS,
1H-NMR and
13C-NMR analyses, as detailed in
Supplementary Material (Figures S2–S7). The
1H-NMR and
13C-NMR spectra clearly showed that the primary OH group in the alkyl chain is the only one involved in the ester product, confirming the selectivity of the enzymatic esterification.
These results show the effectiveness of the combination of biocatalysis and SLILs to achieve the efficient esterification of FFAs with HT. While the exquisite selectivity of the enzymes simplifies and improves the efficiency of this desired transformation, the selection of this SLIL as a non-aqueous green solvent with an excellent solubilization capacity permits us to significantly reduce its contribution to the mass transfer and improves the reaction rate compared to other organic solvents (see
Section 2.5, Table 3, entries 2 and 3) [
15,
21]. Moreover, the potential for recovery and reuse of this SLIL is much more interesting from the economic and environmental points of view. Thus, it has been demonstrated that the synergy between the IL and the biocatalysts is fundamental for the efficient modification of natural bioactive compounds following the selectivity and economy criteria [
13,
14,
15,
16]. However, the excellence of this combo of IL-biocatalysts can be boosted through the optimization of the reaction conditions, attending to the amount of biocatalyst, the reaction temperature and the molar ratio of substrates.
As can be seen in
Table 1 (entries 1–4), the increase in the enzyme amount from 50 to 400 mg provides a concomitant increase in product yield up to 87% (see entry 4). However, it should be noted that the productivity of the reaction systems shows a bell-shaped profile as the amount of enzyme increases, the best results being obtained when using 100 mg N435/mmol HT (see entry 3), a value four times higher than that obtained for the highest enzyme content. Reaction temperature was also shown as an important parameter, being observed a clear improvement in product yield (from 47% to 83%, see entries 2, 5 and 6) when the temperature raised from 60 to 80 °C. This fact was directly related to the greater suitability of the reaction system for dissolving both substrates (HT and Hex) into the ionic net and enhancing their transfer rate to the active site of the enzyme whose activity is maintained by the protective effect of SLIL media [
15]. The ability of hydrophobic SLILs to stabilize enzymes at high temperatures has been widely reported (e.g., up to 1370 days half-life time at 60 °C in the
N-octadecyl-
N’,
N”,
N”’-trimethylammonium bis (trifluoromethylsulfonyl)imide IL) [
14,
22]. This stabilization is attributed to the preservation of the essential water shell around the enzyme within the IL network, which acts as a stabilizing confined space for biocatalyst conformation. It should be noted that by decreasing the HT:Hex molar ratio to 1:2 mol/mol (see entry 7), both product yield (76%) and productivity (2.6 mmol HT-Hex/g N435 h) parameters remained practically similar to those obtained for a 1:4 HT:Hex molar ratio (see entry 2). Consequently, the 1:2 HT-Hex molar ratio was selected for further experiments because of the improvement in green metric parameters of the process (e.g., atom economy) [
11,
23].
2.2. Biocatalytic Synthesis of HT Monoesters with Different Acyl Chain Length
To analyze the suitability of the N435/[C12mim][NTf2] system for the lipophilization of HT, the biocatalytic synthesis of HT monoesters from fatty acids with different alkyl chain length was studied under the optimized reaction conditions.
Figure 2 shows the time-course profiles of the
N-435-catalyzed direct esterification of hexanoic (C6), octanoic (C8), decanoic (C10), lauric (C12), myristic (C14) or oleic (C18:1) acid with HT using a 1:2 HT:FFA molar ratio at 80 °C. For all the assayed reaction systems, the immobilized enzyme was able to achieve a product yield higher than 50% within the first 30 min, whatever the size of the alkyl chain, reaching almost the maximum value in 2 h with a slight increase afterwards (i.e., up to 70–83% HT-monoester yield after 4 h reaction). The greater efficiency of the proposed approach can be observed after a comparative analysis with other strategies previously described, where similar yields were achieved after 16 h reaction by using a transesterification approach of synthesis in acetonitrile as reaction medium [
19]. According to the profiles in
Figure 2, a reaction time of 2 h was selected as the most appropriate for enzymatically producing HT monoesters, attending to the balance between high yield and productivity, as well as minimizing any possible undesired oxidations on HT derivatives induced by heat, that could occur after long reaction times at 80 °C.
Figure 3 shows the evolution of the HT-monoester product yield and the productivity of the reaction system as a function of the alkyl chain length of the carboxylic acid used for the biocatalytic esterification of HT after 2 h of reaction. Both parameters show a similar behavior being increased with the alkyl chain length from hexanoic (C
6) to lauric (C
12) acids and then remained practically unchanged (e.g., approx. 80% yield and 3.8 mmol HT monoester/gN435·h) for myristic and oleic acids as the most hydrophobic cases. Although differences in the performance between the more hydrophobic FFAs were scarce, it can be noted that a slight improvement is obtained with lauric acid. A similar pattern was reported for the N435-catalyzed esterification of FFAs with different alkyl length with glycerol [
13] and panthenol [
17,
23], where lauric acid also displayed the best performance for both, either in SLIL or solvent-free reaction media. For these hydrophobic SLIL-based reaction media, these results clearly demonstrated that the biocatalysts’ performance in the reaction system is positively influenced by the increase in the alkyl chain length of the acyl donor. This improvement is driven by the hydrophobic interactions between the alkyl chains of the FFA and the SLIL [C
12mim][NTf
2], fully aligning with the “like-dissolves-like” principle [
14,
22]. Thus, the best results obtained for lauric acid may be attributed to a favored mass-transfer rate of this fatty acid inside the IL net having the same alkyl chain length, as it was also reported for the case of the biocatalytic synthesis of aliphatic esters in IL/supercritical CO
2 biphasic systems [
24]. It is important to note that, despite the excess of acyl donor respect HT and the increased hydrophobicity of the reaction media with all tested FFAs, the degree of selectivity towards the synthesis of HT monoesters is not affected, not detecting diester products that could signify a decrease in the antioxidant activity. These results emphasized the excellent synergies between biocatalysts and SLILs to achieve the efficient and selective lipophilization of aromatic alcohols [
11,
14].
2.3. Scaling up of the Production of HT-Monohexanoate
To demonstrate the robustness of this procedure, a tempting assay to measure the suitability for scaling up was carried out by increasing 10-folds the reaction mass with respect to the optimized reaction in
Table 1. Under these conditions, the incubation was performed in a reactor with an anchor mechanical stirring, coupled to a vacuum system to remove the water by-product released from the enzymatic reaction.
Figure 4 shows the accumulated productivity (in terms of mmol of HT-monohexanoate per gram of N435) for the N435-catalyzed direct esterification of Hex with 0.5 mmol (low scale) or 5 mmol (high scale) HT by using a 1:2 HT:FFA molar ratio in 70% (
w/w) [C
12mim][NTf
2] at 80 °C. The comparison of the time-course profiles reveals a similar biocatalytic performance in both scales of synthesis and even a slight improvement when the reaction mass is increased 10-fold, reaching a value close to 8 mmol HT-monohexanoate/g N435 at 3 h reaction time. This result was attributed to the better suitability of the mechanical anchor stirring for mixing the resulting viscous reaction medium with respect to the magnetic stirring used for low reaction size. By this approach, an adequate mass-transfer rate during the biocatalytic process occurred, as well as an efficient removal of the water by-product produced along the reaction by the vacuum system coupled to the reactor. These results highlight the relevance of the setup as an additional element to the N435/SLIL system to achieve the best performance. The intensification of the biocatalytic synthesis provided by the suitable setup at high reaction volumes was also observed, although to a greater extent, for the synthesis of panthenyl monolaurate [
23] and xylityl monolaurate [
25] by direct esterification in solvent-free media.
To build green chemical processes, it is necessary to develop integrated approaches for selective (bio)transformation and separation, capable of providing the products directly and the recovery for reuse of all the elements of the reaction system (e.g., biocatalysts, solvents, etc.). The SLILs (e.g., [C
12mim][NTf
2], etc.) are temperature-switchable ionic liquid/solid phases that behave as sponge-like systems that permit us to develop straightforward and clean approaches for product separation after the biocatalytic step by a simple protocol of cooling and centrifugation. By this approach, the SLIL precipitates as a solid salt at the bottom, while the products remain in the upper liquid phase, as pure products when they are liquids or dissolved in another green molecular cosolvent (e.g., water, etc.) previously added [
14,
15,
17,
22]. For this system, the full release of HT-monohexanoate and unreacted HT from the IL matrix could not be achieved by simple cooling and centrifugation of the reaction mixture, as occurred for volatile flavors [
15]. For the proper extraction of these compounds, the addition of propylene glycol:water (PG:H
2O, 85:15
v/v) green solution was necessary, providing a liquid–liquid biphasic system. This mixture was then fully shaken, cooled and centrifuged to precipitate the solid SLIL (bottom phase), while the released HT and HT-monohexanoate were accumulated in the propylene glycol:water phase (upper phase, see
Figure 5). Briefly, five volumes of PG: H
2O (85:15
v/v) were added to 4.5 mL (4.5 g) of the reaction mixture from the biocatalytic step for HT-monohexanoate synthesis in [C
12mim][NTf
2]. From the initial mass of 4.5 g, a total of 1.35 g made of HT-Hex (94%) and unreacted HT (6%) were recovered in the liquid phase. A
19F-NMR analysis (insert in
Figure 5 and
Figure S8) showed the presence of traces of SLIL (up to 1%) that can be fully eliminated by other classical procedures (i.e., ionic exchange column). The precipitated SLIL accounted for 4.2 g and its white color (identical to the pure SLIL) points to almost the total release of the reaction species. Only a content of 10% HT-Hex was still retained in the ionic net, having the possibility to carry out another purification step or to directly reuse this SLIL in another operational cycle.
It should be noted that propylene glycol (PG) meets the specifications of the Food Chemicals Codex (Report Number: 27 NTIS Accession Number: PB265504, 1973) in agreement with the Select Committee on GRAS Substances (SCOGS) [
26]. Because of the safety of PG, the extracted mixture containing the HT monoester could be used without additional steps of purification, contrary to other strategies where the use of volatile organic solvents involves tedious workups that reduce the greenness of the overall process and increase waste.
2.4. Antioxidant Activity of the HT-Monoesters
The industrial interest in preparing lipophilized HT derivatives to be used as nutraceuticals in hydrophobic-based formulations is fully dependent on the maintenance of the antioxidant power with respect to the free HT. The antioxidant activity of HT and its derivatives after the esterification with different alkyl-chain length FFAs was determined by their capacity to reduce the free radical 2,2-diphenyl-1-picrylhydrazyl, which manifests through a color turn from deep purple to pale yellow that can be quantified by Vis-UV spectroscopy at 517 nm. [
11,
27,
28] To carry out this assay, SLIL-free samples were first obtained from the reaction media by liquid–liquid extraction, and their respective concentrations were determined by HPLC using a calibration pattern. Free HT and vitamin C (ascorbic acid) were used as control references of the antioxidant activity, and the concentration of all samples was adjusted to 80 nmol for a proper comparison (see Materials and Methods section). The analysis was performed on a freshly extracted reaction mixture and, after 3 months of storage at 4 °C, was run in duplicate to obtain the mean and standard deviation. Additionally, the capacity of the different HT monoesters for reducing the Fe
3+-specie was determined by means of the FRAP method (see
Table 2).
According to
Table 2, the results obtained by the DPPH assay showed that the relative antioxidant activities of HT and HT monoesters ranged from 89 ± 3.7 to 95 ± 0.5%, being clearly higher than that resulted from the same concentration of vitamin C (49.3 ± 13%). This could be attributed to the double reductive moieties onto the HT structure with respect to the sole reductive group of vitamin C [
29]. Furthermore, it should be noted how all the HT-monoesters derivatives maintain the same antioxidant activity, regardless of the length of the alkyl chain of the FFA, since the selective esterification did not affect the aromatic hydroxyl groups, activity as demonstrated by NMR analysis (see
Figure S7). However, attending to the time-course profile of the DPPH reduction (
Figure 6), a certain slowdown in the reaction rate was detected for HT esters with respect to free HT and vitamin C. This fact had already been reported for the lipophilization of HT [
20,
30], as well as for other aromatic acids (e.g., caffeic acid, coumaric, etc. [
11]), being attributed to a lower ionization of the aromatic hydroxyl groups after the esterification. This slowdown could be responsible for the decay in the antioxidant activity measured at short reaction times (<1 h) in the DPPH method [
28,
31]. Additionally, the DPPH assay of the different HT monoesters stored at 4 °C for three months showed a similar antioxidant capacity, highlighting the stability of the HT monoesters.
Alternatively, an FRAP assay was also used to determine the antioxidant activity of the HT monoesters (see Materials and Method section). The obtained results confirmed a high antioxidant power of these HT monoesters, obtained values between 1.4 and 4.9 µM TE per each nanomole of the sample analyzed, which was also maintained after 3 months at 4 °C. These results push again on the excellent suitability of these compounds as antioxidants. It should be noted that despite the study of the antioxidant stability of HT monoesters is limited due to the short time elapsed, the obtained results are promising for the use of these products as stable antioxidant additives in food preservation conditions.
Thus, the esterification of FFAs with HT not only improves the miscibility with lipophilic formulations in cosmetics or foods, favoring skin penetration and intestinal absorption but also the longer reaction time of HT-monoester derivatives could be considered an advantage to extend the antioxidant activity over time. Thus, the combination of these HT monoesters with other antioxidants with a faster rate (i.e., vitamin C or free HT) could be interesting as a protective system for providing a fast and more prolonged answer against free radicals.
2.5. Green Metric Assessment of the Biocatalytic Synthesis of HT-Monoesters
To assess the sustainability of the biocatalytic strategy here presented, the synthesis of HT-monohexanoate was selected as a representative example of HT monoesters. Using different recognized green metrics, i.e., atom economy (AE), yield (ε), stoichiometric factor (SF), mass recovery parameter (MRP), reaction mass efficiency (RME), process mass intensity (PMI), E-factor and total carbon release (TCR) parameters and the Ecoscale tool, a “gate to gate” analysis has been made comprising the synthesis and workup. The AE, 1/SF and ε parameters provide information about the reactivity of substrates and atoms incorporated into the desired products. It should be noted that the MRP concerns the recyclability of the reaction species (or their contribution to waste), whereas RME is considered a global indicator of sustainability, comprising all the above parameters. The values of all these parameters range between zero to one, corresponding with the highest value to the best sustainability. Alternatively, the E-factor parameter may be used as waste quantification criteria, being expected to have the lowest value for sustainable processes. This E-factor can be extrapolated from the RME or the PMI, being the last parameter used to identify the origin of waste (see
Table S1) and the sensitive steps of further optimization to promote waste reduction. Also, the PMI permits us to calculate the emissions of CO
2 through the total carbon release (TCR) parameter, where a different factor is applied to organic (waste accumulated in the synthesis step) and aqueous (wastewater in the downstream steps) waste to determine the CO
2 production, considering a scenario of waste incineration [
32]. The EcoScale tool provides approximate information about the LCA by considering aspects of the toxicity and hazardousness of the reagents or the energy invested in the whole process of synthesis and purification (see Material and Methods and
Supplementary Material sections for further details) [
11,
23].
For a comparative green analysis, other reported strategies for HT-monoester biocatalytic synthesis were selected as a result of the sufficient information they provided (see
Table 3) [
10,
19,
20]. Among other conditions, the most relevant differences between these approaches concern the use of volatile organic solvents as reaction medium (entries 2–4), as well as aliphatic esters (entries 1 and 2) as activated acyl donors for a transesterification approach, which provides easy solubilization into the solvent that resulted in homogeneous reaction media. In all cases, the reaction was catalyzed by N435, providing excellent yields (75–98%) but different performances. Thus, a high HT-monoester yield (93%, entry 2) was obtained at the shortest reaction time (1.25 h), leading to the highest value of productivity (5.4 mmol ME/g N435 h). These results are slightly higher than those here reported by a direct esterification approach (see entry 4, 3.1 mmol HT monoester/g N435∙h). It can be noted that the use of a very low amount of biocatalyst (33 mg/mmol HT, see entry 3) involves a lengthening in the reaction time up to 48 h for achieving a 75% HT-monoester yield, being the productivity greatly reduced (0.5 mmol ME/g N435 h). In this regard, it seems more appropriate to increase the amount of enzyme to improve esterification reaction rates and productivity.
However, yield and productivity parameters only focus on reaction efficiency, and other critical aspects related to reaction conditions and preparation that provide information on resource use (substrates, energy, solvents, etc.) and waste generation must also be taken into account [
11,
23]. Therefore, a complementary sustainability analysis becomes necessary to identify the most efficient approach. In this regard, the ε was complemented with other green parameters like AE, 1/SF, MRP and RME, which are usually represented as the vertices of a pentagon (
Figure 7). As can be seen, the greenness of the process is shown when a balanced pentagon with a maximum radius of one is obtained, which is the highest value for each metric [
33]. The analysis of these metrics has been strictly referred to as the synthesis step (or upstream) to identify the most efficient reaction conditions.
The AE parameter provides information about the suitability of the strategy selected, revealing the contribution of by-products to the overall synthesis. Thus, the application of an esterification strategy (entries 3 and 4,
Table 3; blue and green lines,
Figure 7) shows the highest values of AE as a result of the release of water as a unique by-product. Although the transesterification strategy provides the release of alcohol as a by-product, the high AE value resulted in entries 1 and 2 is due to the lower molecular mass of ethanol and acetaldehyde by-products, respectively, with respect to the large alkyl chain of the obtained HT-monoester products. As the AE parameter does not consider the substrate’s mass balance in the reaction system, the green analysis must be complemented with the stoichiometric factor parameter (1/SF), which quantifies the excess of substrates with respect to the reaction stoichiometry. Then, an important decay in the 1/SF parameter was obtained for entries 1 and 2 (values of 0.1) due to the great presence of fatty acid esters used as acyl donors. On the contrary, the use of a 1:2 HT:Hex molar ratio (see blue and green lines,
Figure 7) raises the 1/SF parameter to an acceptable value of 0.7. When using an excess of one of the substrates, the contribution to waste is great, being strongly penalized by other green metric parameters. For example, attending to the MRP formula in
Table S1, this excess of substrates is quantified twice, in the 1/SF parameter and in the waste (W) term, having a profound impact on the reduction in the value of the MRP parameter. Also, the use of organic solvents as non-recoverable input or the low reaction yield greatly impacts a poor value of MRP. Conversely, the suitability of SLILs to be recovered and reused [
19,
20,
21,
28], together with the fair molar ratio of substrates used in the strategy here reported, leads to the best MRP value (0.66, entry 4), being 66-folds higher than the MRP value of entry 3 (0.01) despite using the same reaction conditions. The RME parameter collects the results of all the above green metrics to provide an overall landscape of the reaction sustainability and thus, may be considered as the most important parameter in the radial pentagon. As can be seen, whilst the reported strategies (see lines blue, orange and red) adopt a triangle or a square shape because their RME value is almost null (0.01–0.03), the direct esterification of Hex with HT in SLILs (green line) results in an RME value of 0.33, being the only one that fits a balanced pentagon and shows the higher values for almost all the assayed metric parameters.
Alternatively, the determination of the PMI parameter is useful to detect those steps that can be improved for reducing waste. The PMI calculator allows us to determine waste accumulation through the different steps of upstream and downstream. Because of the insufficient information on solvent mass used in the workup in entry 2, the complete analysis of the PMI parameter was only carried out for entries 1, 3 and 4 (see
Table 3).
Figure 8A provides the distribution of the source of waste for each of the selected strategies resulting from the PMI calculator. Although entry 1 is a solvent-free synthetic approach, the high mass of solvents used in the workup tarnishes its sustainability (up to 670 kg input/kg output). It should be noted how the use of a fully recoverable solvent, like SLIL, joined to the high biocatalytic efficiency achieved for entry 4, leads to the best PMI results.
From the PMI parameter, the E-Factor refers to the overall generated waste, while the TCR parameter points to the waste contribution to CO
2 emissions (see
Table S1 and
Figure 8B,C) [
34]. The results obtained for E-factor and TCR follow the same pattern as that observed for the PMI case, pointing again to the negative character of non-recoverable solvents to the environmental burden.
To obtain an overview of the LCA for the synthesis of HT monoesters according to the selected strategies, the analysis was complemented with the EcoScale. Although this tool does not allow for a fine discrimination between reaction conditions, it is very useful to evaluate certain parameters not contemplated in the previous metrics, such as the energy invested, the price and toxicity of the reagents or the stages and equipment necessary for the synthesis and workup. Thus, starting from an initial value of 100% sustainability, penalties are assigned as a function of those criteria that have been collected in detail in
Table S2 (it should be remembered that the workup of entry 2 is incomplete). For entries 1–3, most of the penalties come from the cost and safety of substrates and reagents used. For example, the higher price of the activated acyl donor (i.e., ethyl palmitate and vinyl decanoate) is heavily penalized compared to FFAs. The lower yield obtained in entries 3 and 4 is also penalized, though this tool only considers the yield of the limiting substrate and does not account for the excess substrate used in entries 1 and 2. This is a clear example of the limitations of this tool, together with the rough discrimination between the reaction conditions in the section of technical setup. However, these weaknesses can be counterbalanced by combining this tool with other green metric parameters.
As a result, all the penalties assigned reduce the scores for entries 1–3 from 100% (corresponding to an ideal sustainable reaction) to almost 50%. Meanwhile, the one here reported obtains a value of 77% due to the lower range of reagents and the simplification and safety of the overall process. This punctuation, according to the authors of this tool, corresponds to excellent operating conditions [
35].
In all the green parameters analyzed in this work, the contribution to waste of the SLIL used in this work has been omitted due to its recovery. However, the potential environmental impact of IL versus other volatile organic solvents can be discussed. So far, there are a limited number of LCA studies performed on ILs, which present certain gaps due to the lack of relevant information [
36]. Regarding the case of [C
12mim][NTf
2] SLIL, its low vapor pressure prevents evaporation, while its high hydrophobicity also prevents mixing with aqueous media. This means greater control of its release compared to organic solvents and allows it to be recovered and reused almost entirely over several operational cycles before degradation.