Syuuhei
Komatsu
ab,
Naoki
Kamei
a and
Akihiko
Kikuchi
*a
aDepartment of Materials Science and Technology, Tokyo University of Science, 6-3-1 Niijuku, Katsushika, Tokyo 125-8585, Japan. E-mail: kikuchia@rs.tus.ac.jp
bFaculty of Pharmacy and Pharmaceutical Sciences, Josai University, 1-1 Keyakidai, Sakado, Saitama 350-0295, Japan
First published on 16th November 2024
Most biological materials used in the body undergo protein adsorption, which alters their biological functions. Previously, we introduced surface-degradable hydrogels as adsorbed protein-removing surfaces. However, only a few surface renewals were possible because of the hydrophilic nature of the hydrogels, which accelerated their degradation. In this research, we introduced thermoresponsive properties of hydrogels for limited degradation for protein removal. Hydrogels were synthesized by the radical polymerization of N-isopropylacrylamide (NIPAAm), 2-methylene-1,3-dioxepane, and poly(ethylene glycol) monomethacrylate (PEGMA). The synthesized hydrogels demonstrated thermoresponsive behavior derived from poly(NIPAAm). At 10 °C, the hydrogels swelled and exhibited bulk degradation. After 2 h, the prepared hydrogels were degraded completely. However, at 37 °C, the hydrogels shrunk and showed surface degradation. After 7 h of degradation, the swelling ratio of the hydrogels changed marginally. The proteins adsorbed on the hydrogel surfaces were removed via surface degradation. However, the fluorescence intensity of adsorbed proteins increased on the hydrogel surfaces without degradable functions. In addition, the fluorescence intensity of adsorbed proteins increased in the hydrogels without PEG graft chains, suggesting that the prepared thermoresponsive hydrogels with PEG chains could be used as potential biomaterial surface coating materials, exhibiting regenerative low-fouling ability.
Thus, biomaterial surface cleaning or the removal of adsorbed proteins is important; however, it is generally difficult to construct surfaces that clean regardless of the type of adsorbed protein. Dynamic self-renewing surfaces made of degradable polymers have been used as coating materials for marine-based material surfaces.15,16 The material surfaces exhibit removal properties for marine microorganisms via surface hydrolysis. Hydrophobic materials are often used for surface degradation because they can prevent the penetration of enzymes and/or water inside the materials. However, hydrophobic materials have various drawbacks for use in medical devices, such as adsorption of nonspecific proteins and aggregation of degraded materials. Therefore, the introduction of surface-cleaning properties into biomaterials requires the maintenance of protein removal and the release of hydrophilic oligomers as byproducts after degradation and surface renewal within the lifetime of the material.
We previously reported that poly(2-methylene-1,3-dioxepane (MDO)-co-2-hydroxyethylacrylate (HEA))-g-PEG (poly(MDO-co-HEA)-g-PEG) hydrogels exhibit protein removal properties via hydrolysis of the ester group in the gel surface vicinity.17 This property is realized by the thermoresponsive swelling–shrinking behavior of the base hydrogels. While the adsorbed proteins were removed from the prepared hydrogels, bulk decomposition of the gels occurred over time when the gels were subjected to repetitive protein removal. Poly(MDO-co-HEA)-based hydrogels exhibited liquid–liquid phase separation-type thermoresponsive behavior with a relatively high water content.17,18 The degradable polyester-based particles, PMDO-g-PEG, degrade from the particle surface.19–22 These particles are formed by hydrophobic interactions and decomposed from the particle surfaces by hydrolysis, reducing the particle size. This was due to the aggregation of hydrophobic polymers which suppresses the penetration of water molecules into the particle core, inhibiting bulk degradation. These reports suggest that aggregation of the polymer network is important for controlling the surface degradation of hydrogels. Therefore, we focused on liquid–solid phase separation-type thermoresponsive properties to control the surface degradation of the synthesized hydrogels.
In this paper, thermoresponsive degradable poly(NIPAAm)-based hydrogels are reported, because poly(N-isopropylacrylamide) (PNIPAAm) is a well-known liquid–solid phase separation-type thermoresponsive polymer above the lower critical solution temperature (LCST) and often used as a biomaterial.23–27 The prepared hydrogels showed thermoresponsive swelling–deswelling changes and surface degradable properties in the shrunken state at a physiological temperature of 37 °C. In addition, the adsorbed proteins on the hydrogels were removed through surface degradation (Fig. 1).
Sample | Monomer feed ratio (mol mol−1) | |
---|---|---|
MDO![]() ![]() |
(MDO + NIPAAm)![]() ![]() |
|
1 | 3![]() ![]() |
100![]() ![]() |
2 | 3![]() ![]() |
Without PEGMA |
3 | 0![]() ![]() |
100![]() ![]() |
Swelling ratio [−] = (Ws − Wd)/Wd. | (1) |
SN ratio [−] = Fh/Fg. | (2) |
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Fig. 2 Thermoresponsive properties of the prepared hydrogels. (a) Image of the thermoresponsive behavior of the hydrogels (sample 1 in Table 1). All scale bars are 5 mm. (b) Thermoresponsive behavior in the swelling ratio of the hydrogels (sample 1 in Table 1). Data are expressed as the mean of 3 samples with S.D. |
Next, the degradation abilities of the prepared hydrogels were measured. The degradation abilities were analyzed under alkaline conditions. Fig. 3a shows the change in the degradation time-dependent swelling ratio of the hydrogels (sample 1 in Table 1) in NaOH solution at 10 °C and 37 °C. At 37 °C, the swelling ratio showed a slow increase from 2.2 to 4.8 and maintained a shrunken state after 7 h (Fig. 3b). However, upon degradation at 10 °C, the swelling ratio was substantially increased from 16 to 34, and after 2 h of incubation in NaOH solution, the hydrogels showed complete degradation and dissolved. The slow degradation at 37 °C indicated that surface degradation of the hydrogels would preferentially occur in the shrunken state, rather than degradation occurring both at the surface and inner part of the hydrogels as can be seen at 10 °C; an increase in the swelling ratio of the hydrogels was confirmed within 2 h. These results suggest that degradation in the contracted state may increase the swelling of the gel surface and decrease the polymer density on the surface (Fig. 3c). In our previous reports, thermoresponsive degradable poly(HEA-co-MDO)-g-PEG hydrogels also showed suppression of degradation at 37 °C in a shrunken state.17,19 However, after degradation at 37 °C for 7 h, the swelling ratio increased 6-fold (from 3 to 18). The poly(HEA-co-MDO)-g-PEG hydrogels show liquid–liquid phase separation-type thermoresponsive behavior, which indicates a relatively high water content, even at higher temperatures. In contrast, PNIPAAm exhibits liquid–solid phase separation-type thermoresponsive behavior.23–25 It is suggested that the type of thermoresponsive behavior is responsible for suppressing bulk degradation by hydrolysis effectively at 37 °C in which the hydrogels are in a shrunken state due to the thermoresponsive properties of PNIPAAm chains.
The surface properties of the hydrogels before and after degradation were analyzed by 1H NMR and ATR-FTIR measurements according to a previous study.18 The supernatant solutions were obtained at degradation times of 2 and 5 h and their 1H NMR spectra were obtained to determine the degraded entities in NaOD (1.0 mmol L−1) containing D2O (Fig. 4a). The peak of PEG was observed at 3.75 ppm after 2 h of degradation, and the intensities of the peaks of PEG and the corresponding degraded products of the hydrophilic oligomers increased after 5 h of degradation. These results indicated that the PEG chains cleaved by surface degradation were released from the hydrogels to the external fluid, and the peak derived from PEG intensified with degradation time. Moreover, the hydrogel surfaces during degradation were analyzed using ATR-FTIR (Fig. 4b). The control (neat) hydrogels soaked in NaOH solution for 5 and 7 h were analyzed after freeze-drying. Before hydrogel degradation, the peaks of ether (–C–O–C–), ester (–C(O)–O–), and amide (C(
O)–NH–) groups derived from the corresponding monomer (MDO, PEG, and NIPAAm, respectively) units in the hydrogel chains were observed at 1750, 1150, 1550, and 1650 cm−1, respectively. In addition, these ATR-FTIR peaks were observed even after surface degradation for at least 7 h. The obtained results indicated that the prepared hydrogels have almost the same surface compositions even after degradation, suggesting that the hydrogels show surface renewable ability via re-orientation of PEG chains on the surfaces by degradation. This is in good agreement with the previous studies on the degradation properties of poly(HEA-co-MDO)-g-PEG hydrogels.17 The change in the swelling ratio of the hydrogels during degradation for at least 5 h was mostly constant (Fig. 3a), and the surface characteristics remained mostly unchanged during degradation (Fig. 4a and b), which suggested degradation of the hydrogel surface. In addition, the thermoresponsive properties of the hydrogel degradation products were evaluated based on temperature-dependent transmittance changes (Fig. S1†). The blue line is the transmittance change of neat PNIPAAm, and the LCST appeared at approximately 32 °C. The orange line represents the hydrogel degradation byproducts. The transmittance of the byproducts decreased above 38 °C, indicating that the products were hydrophilic at 37 °C.
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Fig. 4 Degradable properties of the hydrogel surfaces and supernatants recovered during degradation (sample 1 in Table 1). (a) 1H NMR spectra of the supernatants of degraded hydrogels after degradation for 2 and 5 h. (b) ATR-FTIR spectra of the hydrogel surfaces before and after degradation for 5 and 7 h at 37 °C after drying. |
Finally, protein adsorption on the hydrogels and surface renewability of the hydrogels were analyzed using fluorescence microscopy observation. The renewability of the hydrogel surfaces was investigated by measurements of protein adsorption and removal on hydrogel surfaces, repetitively. First, the prepared hydrogels were soaked in either FITC-BSA or FITC-FBN solution for 1 h, followed by agitation and PBS washing at 37 °C. After washing, the protein-adsorbed hydrogels were soaked in NaOH or PBS solution at 37 °C for 1 h. The adsorbed amount of BSA and FBN in the first cycle was 0.76 ± 0.17 μg cm−2 and 0.89 ± 0.06 μg cm−2, respectively. Fluorescence microscopy observation of the FITC-BSA-adsorbed hydrogels was performed at each step of the 5 cycles (Fig. 5). At the first cycle, the fluorescence signal of FITC-BSA was observed on both the hydrogels (Fig. 5a and b; top-left images), which increased with increasing cycle number. After immersion in PBS, the fluorescence from FITC-BSA decreased but remained in each cycle image (Fig. 5a; bottom). As shown in Fig. 5c, the SN ratio increased with increasing cycle numbers because the amount of adsorbed proteins on the hydrogels increased by repetitive immersion in the FITC-BSA solution. In contrast, fluorescence from FITC-BSA was not observed after washing the hydrogels with NaOH solution (Fig. 5b; bottom). In addition, the SN ratio remained unchanged despite the increased number of degradation cycles, and the fluorescence intensities of the hydrogels subjected to surface degradation decreased to equivalent values to those of the sliding glass (Fig. 5d). As the hydrogel surface degraded, the adsorbed proteins were removed and at the same time the byproduct oligomers were released (Fig. 5e). These results indicated that protein removal was effectively achieved, along with surface degradation, at least five times. The protein removal properties of the hydrogels were investigated in detail (Fig. S2†). The same cycle test was performed using a non-degradable thermoresponsive hydrogel, poly(NIPAAm)-g-PEG hydrogel (sample 3 in Table 1), without MDO during polymerization. The prepared hydrogels were soaked in an FITC-BSA solution under the same conditions. Subsequently, the protein-adsorbed hydrogels were soaked in NaOH solution. The SN ratio of the hydrogels increased in the 3rd cycle. This indicated that surface degradation of the hydrogels was necessary for protein removability.
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Fig. 5 Evaluation of protein removal ability (sample 1 in Table 1). (a) Fluorescence images of the hydrogel surface adsorbed with FITC-BSA after each cycle and after soaking with PBS after FITC-BSA adsorption (bottom). (b) Fluorescence images of the hydrogel surface adsorbed with FITC-BSA after each cycle (top) followed by hydrolysis in NaOH solution (bottom). All scale bars: 300 μm. (c) SN ratio of adsorbed FITC-BSA on the hydrogel surface. Red bars: SN ratio of the hydrogel immersed in PBS solution containing FITC-BSA in each cycle. Blue bars: SN ratio of the hydrogel immersed in PBS in each cycle after 1 h of soaking in PBS solution containing FITC-BSA. Data are expressed as the mean ± SD (n = 3, *: p < 0.05). (d) SN ratio of adsorbed FITC-BSA on the hydrogel surface. Yellow bars: SN ratio of the hydrogel immersed in PBS solution containing FITC-BSA in each cycle. Green bars: SN ratio of the hydrogel immersed in NaOH solution in each cycle after 1 h of soaking in PBS solution containing FITC-BSA. Data are expressed as the mean ± SD (n = 3), n.s.: not significant. (e) Schematic illustration of the surface renewal properties of the hydrogels. |
Fig. 6 summarizes the FITC-FBN removal results. In the fluorescence images, the same tendency as that in the case of FITC-BSA was observed (Fig. 6a and b). Although the fluorescence intensity increased compared to that of BSA, FITC-FBN was effectively removed by surface degradation (Fig. 6c and d). These results suggest that protein removal by degradation is effective regardless of the protein type. We then analyzed the effect of the PEG chains on protein adsorption onto the hydrogel surfaces. The same cycle test was performed using the poly(MDO-co-NIPAAm) hydrogels (sample 2 in Table 1) (Fig. S3a and b†). The prepared hydrogels were soaked in either FITC-BSA or FITC-FBN solution for 1 h. Subsequently, the protein-adsorbed hydrogels were soaked in PBS or NaOH solution. The initial amount of BSA adsorbed on the poly(MDO-co-NIPAAm) hydrogels without PEG was lower than that on the hydrogels with PEG graft chains. The swelling ratio of the poly(MDO-co-NIPAAm) hydrogels without the PEG chain was 0.25 at 37 °C which is lower compared to that of the poly(NIPAAm-co-MDO)-g-PEG hydrogels with the PEG chain: 2.2 at 37 °C, as seen in Fig. 3a. This difference could be due to the presence of PEG chains inside the hydrogels that create hydration domains within the hydrogels, leading to the migration of some BSA molecules inside the poly(NIPAAm-co-MDO)-g-PEG hydrogels. However, the SN ratio of the degraded poly(MDO-co-NIPAAm) hydrogels increased with increasing number of cycles compared with poly(NIPAAm-co-MDO)-g-PEG hydrogels. Moreover, the adsorption of FITC-FBN tended to be similar to that of BSA. When PEG was present on the gel surface, the amount of adsorbed proteins remained constant regardless of the number of removals, suggesting that the protein removal ability was maintained due to the hydration effect of the PEG chains and the excluded volume effect. After 5 cycles of degradation, the swelling ratio of the poly(NIPAAm-co-MDO)-g-PEG hydrogels was increased to 4.9 at 37 °C. However, the swelling ratio of the poly(MDO-co-NIPAAm) hydrogels without PEG chains was 0.23 at 37 °C. It is considered that hydrogel degradation was induced by PEG chains owing to the increased swelling ratio. These results suggested that the PEG chains also influenced effective protein removal under these preparation conditions. Therefore, the prepared hydrogel is expected to be applicable as a thermoresponsive degradable hydrogel that exhibits protein removal behavior upon degradation and maintains its surface properties even after degradation.
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Fig. 6 Evaluation of protein removal ability (sample 1 in Table 1). (a) Fluorescence images of the hydrogel surface adsorbed with FITC-FBN after each cycle and after soaking with PBS after FITC-FBN adsorption (bottom). (b) Fluorescence images of the hydrogel surface adsorbed with FITC-FBN after each cycle (top) followed by hydrolysis in NaOH solution (bottom). All scale bars: 300 μm. (c) SN ratio of adsorbed FITC-FBN on the hydrogel surface. Red bars: SN ratio of the hydrogel immersed in PBS solution containing FITC-FBN in each cycle. Blue bars: SN ratio of the hydrogel immersed in PBS in each cycle after 1 h of incubation in PBS solution containing FITC-FBN. Data are expressed as the mean ± SD (n = 3, *: p < 0.05). (d) SN ratio of adsorbed FITC-FBN on the hydrogel surface. Yellow bars: SN ratio of the hydrogel immersed in PBS solution containing FITC-FBN in each cycle. Green bars: SN ratio of the hydrogel immersed in NaOH solution in each cycle after 1 h of soaking in PBS solution containing FITC-FBN. Data are expressed as the mean ± SD (n = 3), n.s.: not significant. |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4bm01383b |
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