Genny Pastorea,
Serena Gabrielli*a,
Teresa Cecchib,
Arianna Giulianib,
Cristina Cimarellia,
Alessandro Menchia and
Enrico Marcantonia
aUniversity of Camerino, School of Science and Technology, Organic Chemistry Division, Via S. Agostino n.1, 62032, Camerino, Macerata, Italy. E-mail: serena.gabrielli@unicam.it
bTechnical Institute Superior, ITT G. e M. Montani of Fermo, Via Girolamo Montani n.7, 63900, Fermo, Italy
First published on 12th March 2021
Among many, poly(lactic acid) (PLA) has received significant consideration. The striking price and accessibility of L-lactic acid, as a naturally occurring organic acid, are important reasons for poly-(L)-lactic acid (PLLA) improvement. PLLA is a compostable and biocompatible/bioresorbable polymer used for disposable products, for biomedical applications, for packaging film, in the automotive industry, for electronic device components, and for many other applications. Formerly, titanium and other metals have been used in different orthopaedic screws and plates, but they are not degradable and therefore remain in the body. So, the development of innovative and eco compatible catalysts for polyester synthesis is of great interest. In this study, an innovative and eco sustainable catalyst was employed for PLLA synthesis. The combined CeCl3·7H2O–NaI system has been demonstrated to be a very valuable and nontoxic catalyst toward PLLA synthesis, and it represents a further example of how to exploit the antibacterial properties of cerium ions in biomaterials engineering. A novel synthesis of poly-(L)-lactic acid was developed in high yields up to 95% conversion and with a truly valuable molecular weight ranging from 9000 to 145000 g mol−1, testing different synthetic routes.
Poly-L-(lactic acid) (PLLA) belongs to the family of polymers commonly made from α-hydroxy acids such as lactic acid (2-hydroxypropionic acid). Three are the main routes usually used to synthetize PLA, depending on the molecular weight of the resulting aliphatic polymer, namely, a direct condensation polymerization, a combined melt polycondensation with a Solid State Process (SSP) starting from oligomers in the presence of tin, titanium or zinc based catalysts,6–11 and the last is the ring-opening polymerization (ROP),12 starting from a purified lactide structure.13,14
Lewis acids have significantly increased their use, and eco-friendly Lewis acid catalysts are available, but particular attention must be directed to their toxicity and to the contamination of the final polymer product especially in the biomedical field. In recent years, multimetallic catalysts are receiving increasing attention in the catalysis of polycondensation reactions that can lead to the formation of polymeric structures.15 A very interesting example is the recent methodology developed by J. A. Garden et al.16 in the use of heterometallic complex catalysts to obtain aliphatic polyesters such as poly(lactic acid). It is a typical academic demonstration of what has been studied in these last decades and namely, that the multimetallic catalysis based on the combined action of different metals in a chemical transformation, amplifies the activity of the single metal. Thus, the proximity between the metal centers, seems to provide favorable conditions for the occurrence of enhanced catalytic properties.17 Up to date, however, this greater catalytic activity, consequence of the heterometallic cooperativity of multimetallic catalysts, is followed by two major application difficulties. First, the assessment of the environmental effects of multimetallic substances requires information on potential combination effects.18 Secondly, the long-term stability of the molecular structures of heterometallic complexes is an omnipresent and pressing concern in industrial processes.19 For the latter reason the most used catalysts in PLA synthesis are the tin(II) salts and the most used are the commercially available SnCl2 or [Sn(Oct)2].20–23 So, the search for useful catalysts for aliphatic polyesters synthesis is a truly big challenge. In the last years, inexpensive, water tolerant, non-toxic,24 and easy to handle cerium trichloride heptahydrate (CeCl3·7H2O) has attracted considerable attention because of its diverse applications as a Lewis acid catalyst in organic synthesis.25 In line with our research interests in exploring new and more concise procedures for polymer formation promoted by Lewis acids, we have increased the potentialities of the combination of CeCl3·7H2O with NaI,26 capable of transforming the typical aggregates of metal halides such as CeCl3 into the corresponding more reactive monomeric structures.27 In addition to our knowledge on the efficiency of CeCl3·7H2O–NaI system, Fedynshkin et al. reported the oligo-lactic acid thermal decomposition promoted by CeCl3·7H2O,28 suggesting us that the use of an appropriate amount of catalyst CeCl3·7H2O–NaI can facilitate the synthesis of the corresponding polyester. Thus, we tested a new, efficient and eco-sustainable CeCl3·7H2O–NaI catalyst following two different reaction processes. Our catalytic procedure (Scheme 1) demonstrated to be very efficient in a two-step synthesis of poly-(L-lactic acid) 4 starting from a polycondensation step in which a prepolymer oligo-(L-lactic acid) (OLLA) 2 has been obtained, followed by a CeCl3·7H2O–NaI melt-solid state (SSP) polycondensation that provides PLLA 4 with a molecular weight ranging between 2000 and 146000 g mol−1. Furthermore, we defined a new strategy for PLLA synthesis, starting from L-lactide 3, using the same cerium(III)–NaI catalytic system for the ring opening polymerization reaction under microwaves irradiation, which provides a polymer in a high percentage of conversion and very good molecular weights, boosting the reaction rate up to 1 hour.
Scheme 1 General synthesis of PLLA using CeCl3·7H2O–NaI as catalytic system with m < n, and cerium(III) salts-sodium iodide activation of the ester group reported by Marcantoni et al.29,30 |
Fig. 1 Crystal structure of CeCl3·7H2O. The Ce coordination polyhedral are shaded in yellow, oxygen atoms are in red, chlorine atoms are in green, and hydrogen atoms are in blue. |
This remarkable ability of water of crystallization can find explanation in its coordination that makes easy the disaggregation of the crystal lattice of cerium salt which might lead to a notable increase in the Lewis acidity of the cerium available at the particle surface.33 This hydrophobic amplification concept34 have been shown in several catalyzed CeCl3·7H2O organic transformations.35,36 To confirm the mechanistic role of the NaI we have analyzed the interaction between CeCl3·7H2O with NaI by X-ray photoelectron spectroscopy, in order to analyze the chemical shift in the core level binding energies.37 Fundamental reasons for this are the inherent element specificity of the associated element core level binding energies, and also the sensitivity both to the amount of the element present and its localization at the surface, the latter characteristic caused by the short mean free path of low energy (30–1000 eV) photoelectrons in the solids.38,39 We have started from a belief that CeCl3 is a rare-earth trihalides whose initial state is f1 (Ce = [Xe]4f15d16s2) as no promotion of f electron is required for a trivalent bonding with chlorine. Nevertheless, in the final state the charge transfer energy defined as the energy required to take an electron from the ligand p level to the unoccupied 4f level (about 9.7 eV)40 (f2v) is less than the value of the 4f-core hole Coulomb attraction (12.2 eV). This leads to a f2v satellite (where v is the hole in the valence) at about 3.4 eV lower binding energy. Intensity and energy of this satellite are sensitive to the degree of hybridization of the f states with the conduction states.41 We reported the XPS measurements42 of the 3d core level in CeCl3·7H2O and CeCl3·7H2O–NaI (Fig. 2 in (a) and (b) respectively).
From the present study we cannot observe a variation within few percent in the intensity of the f2 satellite, indicating that the introduction of the NaI in the system does not vary the degree of the hybridization of the f states with conduction states. Such as hybridization is certainly enhanced for both samples with respect to the only CeCl3 molecular structure,43 but this property is conserved after the insertion of NaI. Furthermore, it can be excluded the presence of an initial f0 (metallic) state due to the promotion of the “f” electron in the valence bond (Fig. 2). Such a peak is in general observed at 10 eV higher binding energies. These results, thus, suggest us that there is not a direct interaction between cerium(III) site and iodide ion. The activity of CeCl3·7H2O–NaI system is mainly exerted in the heterogeneous phase and, above all, we believe that a chloro-bridged oligomeric structure of CeCl3·7H2O is easily broken by donor species such as iodide ion. The resulting monomeric CeCl3·7H2O–NaI complex is a more active Lewis acid promoter.
(1) |
The polymerization conversions are reported in Table S1† with different Lewis acids. In Table S1† it is also reported the onset temperature (Ton) (Fig. S2†). The highest value obtained was around 270 °C, confirming the low molecular weight of 2. The best results were obtained with monomeric CeCl3·7H2O–NaI combination (Table S1,† entry S1g) being this catalyst able to coordinate oxygen atoms and to push the reaction to the elimination of water. Then, different iodide sources were screened in order to ensure the high catalytic activity of cerium(III) Cl3–NaI couple, KI and CuI gave lower efficiency than that of the CeCl3·7H2O–NaI system (Table 1).
The NaI gave the optimal results, so then the ratio between CeCl3·7H2O and NaI was tested and an equimolar ratio allowed to reach the best result (Fig. S3,† CeCl3·7H2O:MxIy → 0.1:0.1 mol%).
The optimized catalytic procedure with CeCl3·7H2O–NaI was subsequently employed in melt-solid polycondensation,45,46 starting from oligolactic acid 2 (OLLA) and carrying out the polycondensation of OLLA in the presence of our CeCl3·7H2O–NaI catalytic system. Through a screening of the ratio between CeCl3·7H2O and NaI (Table 2) it was possible to prepare the aliphatic polyester with high molecular weight and with excellent conversions. The thermal dehydration without a catalyst did not result in a high molecular weight PLLA (Table 2, entry 2a). A high amount of CeCl3·7H2O–NaI (Table 2, entry 2f–h), was able to activate the dehydrative equilibrium. However, due to the hard reaction conditions, such a high concentration of the catalyst, relatively high temperature and long reaction time, induced L-lactide formation and relevant polymer decomposition rather than polycondensation. The results indicated in Table 2 entry 2c, show a weight average molecular weight of Mw = 48300 g mol−1 as the highest molecular weight obtained in the melt polycondensation with a degree of polymerization (DP) equal to 1.08. This value was obtained after 7 h at 180 °C keeping pressure at 1333 Pascal and 0.7 wt% of CeCl3·7H2O. In Table 2 is also reported the onset degradation temperature (Ton) obtained from TGA. PLLA with the highest molecular weight showed a value around 300 °C (Table 2, entry 2c). Ton of the other polymers were lower except when the temperature of polymerization was 200 °C (Table 2, entry 2g). This behaviour could be explained considering all the degradation processes that might occur at high temperatures which led to the formation of shorter chains but also to the subsequent crosslinking of polymer matrixes. PLLA synthetized by melt polycondensation underwent a second step of Solid State Polymerization (SSP).
Entry | Catalystb (wt%) | Temp. (°C) | Time (h) | Mnc (g mol−1) | Mwc (g mol−1) | Tond (°C) | Yielde (%) | DPc |
---|---|---|---|---|---|---|---|---|
a Solid state polymerization (SSP) starting from entry 2c Mw = 48300 Da.b Wt% of OLLA:CeCl3·7H2O:NaI (100:0.7:0.7).c GPC analysis (triple detector).d TGA analysis.e Yield (%) calculated by the equation yield = [g PLLA/g LLA] × 100. | ||||||||
2a | — | 180 | 7 | 7500 | 8000 | 241 | 95 | 1.10 |
2b | 0.3 | 180 | 7 | 8000 | 8300 | 291 | 92 | 1.03 |
2c | 0.7 | 180 | 7 | 44500 | 48300 | 300 | 92 | 1.08 |
2d | 0.7 | 160 | 7 | 16100 | 30000 | 277 | 93 | 1.85 |
2e | 0.7 | 180 | 3 | 24300 | 28900 | 269 | 95 | 1.20 |
2f | 1.3 | 180 | 7 | 11500 | 14500 | 284 | 92 | 1.25 |
2g | 0.7 | 200 | 7 | 7300 | 33700 | 306 | 79 | 4.70 |
2h | 0.7 | 180 | 14 | 16500 | 29900 | 281 | 93 | 1.81 |
2la | — | 150 | 16 | 52400 | 94500 | 305 | 92 | 1.80 |
2ma | — | 150 | 29 | 23200 | 146000 | 310 | 92 | 6.30 |
In particular, PLLA with the highest Mw = 48300 g mol−1 (Table 2, entry 2c), was then underwent the last step (Scheme 2), a solid state process, at 150 °C under reduced pressure. A further recrystallization with diethyl ether (Et2O) was carried out at room temperature. Kinetic studies were performed, after 16 h the PLLA 4 obtained reached an Mw = 94500 g mol−1 with a DP value of 1.80 (Table 2, entry 2l) while, increasing to 29 h this value was equal to 6.30, due to an important decrease in Mn = 23300 g mol−1, even if the Mw increases up to the value of Mw = 146000 g mol−1 (Table 2, entry 2m) (Fig. S4†).
It was shown that the PLLA polymer synthesized by a two-step condensation polymerization of L-lactic acid in the presence of our CeCl3·7H2O–NaI system had significantly higher molecular weight and crystallinity as compared with PLLA produced with the conventional stannous-based catalyst. Discoloration was effectively inhibited by our cerium(III) catalytic system, and there was no significant change in its Tg.
Following the previous study, we carried out the reaction in batch conditions comparing the only CeCl3·7H2O with the multimetallic system (0.1 mol%), without the need of any co-initiator, obtaining a better result with the second one, Mw = 11500 Da and Mw = 15300 respectively (Table 3), in 12 h at 165 °C.
After the first trial with the combined system, a further screening of co-initiators was developed. As shown in Table 4 several alcohols were tested but the benzyl alcohol was the most promising with a Mw = 18100 Da (Table 4, entry 4b), using 3 mol% for these first experiments.
Entry | Co-init.a (mol%) | Mnb (g mol−1) | Mwb (g mol−1) | DPb | Tonc (°C) | Conv.b (%) |
---|---|---|---|---|---|---|
a 3 mol% of co-initiator.b GPC analysis (triple detector).c TGA analysis. | ||||||
4a | 1-Dodecanol | 4700 | 6700 | 1.40 | 273 | 96 |
4b | Benzyl alcohol | 16700 | 18100 | 1.20 | 283 | 93 |
4c | Ethylene glycol | 4700 | 8300 | 1.70 | 281 | 95 |
4d | 1,4-Butandiol | 1500 | 3300 | 2.10 | 274 | 94 |
A kinetic study was performed in order to ensure a good quality of the method and the best result was obtained after 12 h (Table S2†) at 165 °C even if other reaction temperatures were examined (160–170 °C).
In order to increase the reaction rate and make the whole process greener under an energetically perspective, we switched to microwaves.47–49 We maintained the same reaction conditions but the reaction time resulted to be reduced from 12 h to 1 h. The best upshot was reached after 1 h at 165 °C as shown in Table 5 entry 5b with an Mw = 24500, (see kinetic studies in ESI, Fig. S5†).
A further optimisation was performed in order to evaluate the ideal amount of the co-initiator, joint to the new catalytic system. The best reaction environment was obtained using 1.5 mol% of BnOH (Table 6, entry 6f).
Entry | BnOH (mol%) | CeCl3·7H2O–NaIa (mol%) | Mnb (g mol−1) | Mwb (g mol−1) | Tonc (°C) | Conv.b (%) |
---|---|---|---|---|---|---|
a CeCl3.7H2O–NaI equimolar ratio.b GPC analysis (triple detector).c TGA analysis. | ||||||
6a | 3 | — | 3500 | 3600 | 206 | 4 |
6b | 3 | 0.1 | 23400 | 26000 | 250 | 96 |
6c | 3 | 0.2 | 30500 | 31000 | 285 | 93 |
6d | 3 | 0.3 | 7000 | 7500 | 286 | 95 |
6e | — | 0.2 | 11000 | 11100 | 255 | 45 |
6f | 1.5 | 0.2 | 39000 | 40000 | 290 | 97 |
6g | 0.75 | 0.2 | 24000 | 28500 | 286 | 91 |
Footnote |
† Electronic supplementary information (ESI) available: XPS analysis, experimental details, NMR, FTIR GPC and TGA analysis, further optimization studies and kinetic informations. See DOI: 10.1039/d0ra10637b |
This journal is © The Royal Society of Chemistry 2021 |