1. Introduction
Biodegradable materials, due to properties such biodegradability, non-immunogenicity, and biocompatibility with living tissues, are used, among others, in the biomedical field. Aliphatic polyesters belong to the group of the most dynamically developing polymer materials, showing degradability in biological systems. These polyesters are both naturally occurring and synthetically produced [
1,
2,
3,
4].
The speed of the biodegradation process depends on many factors, such as the pH of the environment, the presence of microorganisms, and the specific properties of the polymers used [
5]. Molecular weight, stereochemistry, crystallinity, hydrophobic and hydrophilic interactions, and copolymerization also have a significant impact on the speed of the biodegradation process [
6,
7,
8].
Among the aliphatic polyesters, poly(ɛ-caprolactone) P(ɛ-CL), polylactide (PLA), polyglycolide (PGA), and a copolymer of lactide and glycolide (poly(lactide-
co-glycolide) (PLGA)) can be distinguished due to their excellent biocompatibility, biodegradability and mechanical strength. These polymers have been approved by the United States Food and Drug Administration (US FDA) for use in tissue engineering and drug delivery [
9]. P(ɛ-CL) is a semi-crystalline polyester with a melting point of 58–65 °C, a T
g between 65 °C and −60 °C, and a high solubility in organic solvents. [
10] Due to its low degradation rate, P(ɛ-CL) is used as a material for long-term controlled drug delivery. [
11] Mixtures of polycaprolactone with other polymers alter the rate of degradation, in addition to many other properties, which broadens the potential to use P(ɛ-Cl) copolymers in a range of different applications [
12]. Poly(d,l-lactide) (PDLLA) is an amorphous polymer, due to the random positions of the two isomeric forms along the polymer chain, and has a T
g of approximately 50–60 °C [
10]. The rate of degradation depends on the molecular weight and the crystallinity of the polymer as well as the porosity of the matrix. Relative to PGA, PDLLA is more hydrophobic, which translates into a slower degradation rate [
13,
14]. PGA is a highly-crystalline polymer with a melting point of 200–233 °C and a glass transition temperature (T
g) of approximately 35–45 °C [
10]. Due to its high crystallinity, PGA shows good mechanical properties but also very low solubility, in common organic solvents. Despite its many advantages, the use of PGA is limited due to the high rate of polymer degradation and low solubility, combined with the accumulation of acidic degradation products that can lead to inflammatory reactions. In the case of PLGA, the mechanical and degradation properties are adjusted by the appropriate monomer ratio [
15,
16].
Degradation of polyesters can take place biologically through a range of enzymes, such as lipase, proteinase K, pronase and bromelain, as well as chemically through both transesterification and hydrolysis in either acidic or basic solutions [
17,
18]. Gan et al. investigated the enzymatic degradation of P(ε-CL)/PDLLA blend films in a phosphate buffered saline (PBS) containing
Pseudomonas (PS) lipase. The degradation was stopped after 6 days, when the film weight loss reached 50%. Studies have shown that only PCL in the blends was degraded [
19]. Liu et al. investigated the enzymatic degradation of PLLA, PCL and PLLA/PCL blend films (PLLA/PCL composition 75/25, 50/50 and 25/75), using proteinase K and
Pseudomonas cepacia lipase. They showed that PLLA amorphous domains are degraded using proteinase K; however, this enzyme did not degrade PCL and crystalline PLLA. Unlike proteinase K,
PS lipase degraded both crystalline and amorphous PCL, but not PLLA [
1]. Lin et al. investigated the enzymatic degradation of polycaprolactone-
graft-polyethylene glycol (PCL-
g-PEG) hydrogels in a PBS solution containing
PS lipase over a period of 10 days. Depending on the amount of lipase, hydrogels degraded from three (1 mg/mL lipase) to 10 days (0.05 mg/mL lipase) [
20]. In turn, Dong et al. degraded the terpolymer of L-lactide/1,3-trimethylene carbonate (TMC)/glycolide (P(LLA-TMC-GA)) and its composites with PLGA fibers. The degradation was performed at 37 °C in Tris buffer (pH 8.5) containing proteinase K for 30 days. They found that the rate of enzymatic degradation of PLLA-TMC-GA terpolymers with the dominant LLA component was affected by both the mean LLA block length and crystallinity [
21]. Ding et al. investigated the enzymatic degradation of amphiphilic multi-block poly(ε-caprolactone urethane)s, depending on the amount of poly(ethylene glycol) (PEG) addition. The degradation was carried out in PBS solution, with the addition of AK lipase. The rate of degradation slightly increased with the content of PEG, which yielded increased hydrophilicity, reduced crystallinity and reduced melting points [
22]. Jiang et al. studied enzymatic degradation of single PCL crystals and amphiphilic PCL-
b-PEO-b-PCL and PCL-b-PEO-FG (functional groups FG = NH
2, OCH
3). The degradation was performed in PBS, with the addition of PS lipase [
23]. Blackwell et al. investigated the enzymatic degradation of star-shaped PCL with various central units. Potassium phosphate buffer (0.2 M) and enzymes such as PS lipase and cutiase from
Thermobifida cellulosilytica were used for the degradation. Out of all polymers, the Y-shaped miktopolymer showed the fastest rate of enzymatic degradation, using both cutinase and lipase enzymes [
24].
This article presents the results of enzymatic degradation of amphiphilic miktoarm star-shaped polymers containing hydrophilic (PDMAEMA) and hydrophobic (P(ɛ-CL) PLA, PLGA) segments. Polymers were obtained by an “in-out” approach. To the best of our knowledge, based on the current literature, the degradation of miktopolymers with given composition with PS lipase has not yet been investigated. The main goal of the research was to establish preliminary structure−degradation relationships.
2. Materials and Methods
2.1. Materials
Anisole (Alfa Aesar, 99%, Warsaw, Poland), methanol (Chempur, p.a., Piekary Śląskie, Poland), ethyl α-bromoisobutyrate (EBiB, Aldrich 98%, Poznań, Poland) and N,N′-dimethylaminoethyl methacrylate (DMAEMA, Aldrich, 98%, Poznań, Poland) were stored over molecular sieves in a freezer under nitrogen. Glycerol dimethacrylate (GDMA, Aldrich, Poznań, Poland) was stored in a freezer under nitrogen. ε-Caprolactone (ɛ-CL, Alfa Aesar, 99%, Warsaw, Poland) and toluene were distilled prior to use and stored over molecular sieves. Glycolide (GL, Aldrich, 99%, Poznań, Poland), 3,6-dimethyl-1,4-dioxane-2,5-dione (D,L-lactide, Aldrich, 99%, Poznań, Poland) and N,N,N′,N″,N″-Pentamethyldiethylenetriamine (PMDETA, Aldrich, 99%, Poznań, Poland) were used as received, without purification. Copper(I) chloride (CuCl, Fluka, 98%, Steinheim, Germany) was purified by stirring in glacial acetic acid, followed by filtration and washing with ethanol and diethyl ether. Subsequently, the solid was dried under vacuum. Tin(II) bis(2-ethylhexanoate) (Sn(Oct)2, Alfa Aesar, 96%, Warsaw, Poland) was distilled prior to use. Tetrahydrofuran (THF, Aldrich, HPLC, Poznań, Poland), n-heptane (Chempur, 99%, Piekary Śląskie, Poland) and methylene chloride (CH2Cl2, Chempur, 99%, Piekary Śląskie, Poland) were used as received. Lipase from Pseudomonas cepacia (PS Lipase, ≥30 U/mg) was purchased from Sigma Aldrich (Poznań, Poland).
2.2. Synthesis
2.2.1. Synthesis of Star-Shaped Macroinitiator (MI)
Star-shaped macroinitiators were synthesized via atom transfer radical polymerization (ATRP).
In the first step, the ATRP reaction for DMAEMA was performed. For this purpose, the monomer (DMAEMA—5 mL, 29.67 mmol) was introduced into the Schlenk-type reactor, under a constant supply of argon gas. The solvent (anisole—75% by volume of monomer) and initiator (ethyl α-bromoisobutyrate (EBiB)—49 μL, 0.33 mmol) were then added. After the ligand (PMDETA—69 μL, 0.33 mmol) was introduced, the mixture was subjected to a freezing and degassing process in liquid nitrogen. After freezing and degassing the reaction mixture three times, the catalyst (CuCl—32.64 mg, 0.33 mmol) was added and the reactor was placed in an oil bath. The process was carried out at a temperature of 45 °C. When the DMAEMA conversion was in the targeted range (80–90%), a crosslinker (GDMA) was introduced into the reaction mixture, which was first subjected to a freezing and degassing process in liquid nitrogen. The reaction was terminated 30 min after the introduction of GDMA due to the significant increase in the viscosity of the reaction mixture. The reaction system was deactivated by supplying air to it by opening the reactor. The reaction mixture was diluted with dichloromethane and passed through an alumina chromatography column to remove the catalyst before concentrating the solution by evaporation. The polymer was precipitated in n-heptane and dried to a constant weight.
The PDMAEMA macroinitiators (MI1 and MI2) were obtained as white powders, with yields above 90%.
IR: ν = 3650–3090 cm−1 (νOH); ν = 3050–2840 cm−1 (m, νCH); ν = 2840–2700 cm−1 (m, νCH, next to the amino group); ν = 1825–1640 cm−1 (s, νC=O); δ = 1517–1300 cm−1 (δCH); ν = 1285–890 cm−1 (νCO and νCN).
1H NMR (600 MHz, CDCl3, δ): 4.10–4.00 (2H, s, -O-CH2-); 2.61–2.53 (2H, s, -CH2-N(CH3)2); 2.35–2.25 (6H, s, -N(CH3)2); 2.10–1.75 (2H, m, -CH2-); 1.15–0.80 (3H, m, -CH3).
2.2.2. Synthesis of Miktopolymers
Due to the presence of hydroxyl groups in the core of the star macroinitiator, the ROP reaction of selected cyclic esters was carried out.
A cyclic ester (ε-CL, LA or LA and GA) and a macroinitiator ((PDMAEMA)n-PGDMA) were placed in the Schlenk reactor. Following this process, the solvent (toluene for LA and LA and GA—9% by weight of monomer) and the catalyst (Sn(Oct)2) were introduced. The reactor was placed in an oil bath at 130 °C (ɛ-CL) or 90 °C (LA and LA and GA). The reaction was complete after 1.5 h (ɛ-CL) or 22 h (LA and LA and GA). After termination of the reaction, the reaction mixture was diluted with dichloromethane. The crude product was precipitated in cold methanol and dried to a constant weight. The last step was repeated twice to remove the unreacted macroinitiator.
The resulting miktopolymers were white powders with yields above 80%.
IR: ν = 3650–3090 cm−1 (νOH); ν = 3050–2840 cm−1 (m, νCH); ν = 2840–270 cm−1 (m, νCH, next to the amino group); ν = 1825–1640 cm−1 (s, νC=O); δ = 1517–1300 cm−1 (δCH); ν = 1285–890 cm−1 (νCO and νCN).
1H NMR (600 MHz, CDCl3, δ) for Miktopolymer1 (MP1): 4.10–4.00 (2H, t, -O-CH2-); 3.65–3.60 (2H, -CH2-OH); 2.60–2.54 (2H,s, -CH2-N(CH3)2); 2.35–2.25 (2H, m, -C(O)-CH2-); 1.68–1.60 (4H, m, -C(O)-CH2-CH2-CH2-CH2-); 1.41–1.34 (2H, m, -C(O)-CH2-CH2-CH2-CH2-); 1.15–0.80 (3H, m, -CH3).
1H NMR (600 MHz, CDCl3, δ) for Miktopolymer2 (MP2): 5.28–5.10 (1H, m, -CH(CH3)-O-); 4.22–4.44 (1H, q, -CH(CH3)-OH); 1.62–1.44 (3H, m, -CH3).
1H NMR (600 MHz, CDCl3, δ) for Miktopolymer3 (MP3): 5.28–5.10 (1H, m, -CH(CH3)-O-); 4.92–4.56 (2H, m, -CH2-O-); 4.22–4.44 (1H, q, -CH(CH3)-OH); 3.76–3.79 (2H, m, -CH2-OH); 1.62–1.44 (3H, m, -CH3).
The amounts of the reagents used in the reaction are shown in
Table 1.
2.3. Characterization
2.3.1. Nuclear Magnetic Resonance (1H NMR)
1H NMR spectra of the synthesized polymers solutions in deuterated chloroform (CDCl3) were collected using a Varian Inova 600 MHz spectrometer (Palo Alto, CA, USA) at 25 °C, with TMS as an internal standard. The samples were prepared by dissolving about 10 mg of the test substance in 0.5 cm3 CDCl3.
2.3.2. Attenuated Total Reflectance-Fourier Transform Infrared Spectroscopy (ATR-FTIR)
ATR-FTIR analysis was carried out with a Perkin-Elmer Spectrum Two 1000 FT-IR Infrared Spectrometer with an option of attenuated total reflection (ATR) (Perkin Elmer, Waltham, MA, USA). Spectra were recorded at 16 scans per spectrum and 4 cm−1 resolution in the range of 4000–400 cm−1.
2.3.3. Differential Scanning Calorimetry (DSC)
Thermal analysis was performed on the obtained compounds before and after degradation using Mettler-Toledo 821e STAR and Mettler-Toledo DSC3 differential scanning calorimeters equipped with an XS105DU analytical balance (Greifensee, Switzerland).
DSC measurements were performed before and after degradation. A total of 10 mg of the sample was used for measurements. The samples were placed in 40 μL aluminum standard crucibles with a lid and pin. The temperature range was from −5 °C to 100 °C (MI1 and MI2), −90 °C to 100 °C (MP1) and −30 °C to 200 °C (MP2, MP3), with a heating rate of 10 °C per minute.
The melting enthalpies for the MP1 were determined. Equation (1) was used to calculate the crystallinity of PCL.
where ΔH
m is the enthalpy of melting and ΔH
m° is the enthalpy of melting of the 100% crystalline polymer (139 J/g) [
24,
25].
2.3.4. Gel Permeation Chromatography/Size Exclusion Chromatography (GPC/SEC)
The molecular weight distributions (Đ) and average molecular weights (Mn, SEC) were determined by a size exclusion chromatograph (SEC, 1100 Agilent 1260 Infinity) (Santa Clara, CA, USA). The instrument had an isocratic pump, autosampler, degasser, column thermostat and MDS RI Detector differential refractometer. Data analysis software Addon Rev. was used for data collection and processing B.01.02 (Agilent Technologies). Based on a calibration using linear polystyrene standards (580–300,000 g/mol), the molecular weight was calculated. For separation, a pre-column guard 5 µm 50 × 7.5 mm and two columns (PLGel 5 µm MIXED-C 300 × 7.5 mm and PLGel 5 µm MIXED-B 300 × 7.5 mm) were used. The measurements were carried out in THF (HPLC grade) as the solvent at 40 °C with a flow rate of 0.8 mL/min.
2.3.5. Enzymatic Degradation
Enzymatic degradation was carried out for obtained miktopolymers. First, approximately 10 +/−0.5 mg of each polymeric sample (white dry powder) was weighed in glass vials. In addition, to these vials 0.1 mg of PS Lipase and 5 mL of PBS solution at pH 7.4 with addition of sodium azide (23 μM), which protected the buffer against microbial growth, were added. The vials and their contents were sealed and placed on a shaker with 150 rpm at a temperature of 37 +/−2 °C. Samples were taken out of the incubator at predetermined time intervals, i.e., 1, 3, 5, 7, 14, 21 and 28 days, then frizzed and lyophilized. Samples were analyzed in triplicate. The degree of polymer degradation was calculated from the 1H NMR spectroscopy, and the theoretical values of the number average molecular weight of the degradable polyester chains were determined. In case of MP1 and MP2, the degree of polymerization (DP) of the ε-CL or LA was calculated based on the signal from polyester and the signal from the end group. In the case of P(ɛ-CL), signals from the methylene group in the main chain (δ = 4.10–4.00 ppm) and signals from the methylene group connected to the hydroxyl end group (δ = 3.65–3.60 ppm) were used. Whereas for PLA, the signal from methine group at shifts δ = 5.28–5.1 ppm (repeating unit) and δ = 4.28–4.30 ppm (end group) was taken into account.
In case of MP3, the DP of LA and GA was calculated from the 1H NMR spectrum of the sample taken from the reaction mixture at the end of the reaction.
4. Discussion
The amphiphilic miktoarm star-shaped polymers, based on poly(di)methacrylates and polyesters, were synthesized and characterized. The analysis of
1H NMR and ATR-FTIR indicates that hydrophobic chains dominate the polymer compositions, which, in turn, affects the solubility of the obtained polymers. The molecular weight distribution of the polymers was in the range of 1.2–1.5, which proves that they were obtained in a
δ controlled manner. The highest molecular weight distribution value is found in a polymer that has polyglycolide in its structure. The difference of hydrodynamic volumes between PS standards and branched DMAEMA/polyester copolymers caused the decrease of M
n, SEC values, which are apparent molecular weights. Moreover, there were two different macroinitiators used in the synthesis of miktopolymers. The MI1 has shorter PDMAEMA arms than MI2; thus the M
n, SEC is slightly higher. The obtained miktopolymers had lower M
n,SEC values compared to their macroinitiators (
Table 2,
Figure 4) due to the higher affinity of hydrophobic polyester part to the stationary phase of the column (PS crosslinked with divinylbenzene). The thermal analysis showed that the presence of compounds with different physicochemical properties in the polymer structure is of great importance in the determination of their thermal properties, such as the T
g and T
m.
Enzymatic degradation is affected by the way the enzyme interacts with the polymer chains. Physicochemical properties such as molecular weight, structure, crystallinity and properties of the enzyme, i.e., activity, concentration and stability, also influence the rate of degradation [
29]. The thermograms of miktopolymers after degradation showed that the T
m slightly increased. Enzymatic degradation primarily occurring in amorphous regions of the polyester chains should cause a decrease of T
g. In our case, the T
g increased, and for MP2 and MP3 samples, the additional peak from relaxation enthalpy appeared. This might be a result of the increase of the PDMAEMA fraction and slight reordering of the amorphous phase of the sample [
30]. The degree of crystallinity decreased to 37% after seven days of degradation. The decrease in the degree of crystallinity could be caused by several factors, including a high initial degree of crystallinity, the appearance of oligomers or a decrease in the length of the crystallizable block [
31,
32]. However, there are articles in which researchers claimed that the crystallinity of polyesters increases with increasing degradation time [
33,
34]. Unfortunately, the phase separation in thermograms of miktopolymers was not observed due to the overlap of T
g signal from PDMAEMA part with the T
m signal from polyester arms.
The enzymatic degradation in measurement of both the average weight loss of the sample and % mass loss based on
1H NMR spectroscopy showed that P(ɛ-CL) degrades faster than PLA and PLGA. Blackwell et al. investigated enzymatic degradation using PS lipase of star P(ɛ-CL) with different central units. They showed that the polymer degrades faster with increasing content of the hydrophilic compound [
24]. Moreover, Liu et al. proved that PS lipase can degrade both amorphous and crystalline PCL but cannot degrade PLLA [
1]. Since we used 50:50 racemic mixture of D- and L-lactide for the synthesis of MP2 and MP3, the obtained miktopolymers underwent degradation to a lesser extent. In the case of PLA and PLGA, the degradation rate largely depends on the copolymer composition. Since, according to the literature, the presence of GA repeating units hinders the degradation of PLGA by PS lipase, the degradation rate of MP2 and MP3 was lower in comparison to MP1, due to the presence of D-lactide or glycolide [
29,
35]. In the case of our research, the presence of the hydrophilic segment in the polymer molecule affected the degradation rate. Moreover, degradation of polyesters can take place by autocatalytic hydrolysis [
36]. We assume that hydroxyacids, which are the products of polyester degradation, enhanced protonation of the secondary amine groups in PDMAEMA, causing the electrostatic repulsion and higher affinity of PDMAEMA arms to water molecules. The increase in mass loss of PCL in MP1 and PLA in MP2 after seven days of the experiment can be explained by loosening of the miktopolymers structure and improved contact with the enzyme (
Figure 7).
Degradable polymers degrade at a range of rates, due to different degrees of crystallinity, different molecular weights, the presence of cross-linking bonds, and hydrophobic or hydrophilic character. Additionally, the presence of arms with amine functional groups in the miktopolymers structure may facilitate the process of polyester degradation and increase the spectrum of potential applications of the obtained polymers.