Giang H. Le*ab,
Duong A. Thanha,
Trang T. T. Phama,
Quang Vinh Tranab,
Nhiem Ngoc Daobc,
Kien Trung Nguyen
c,
Són Tung Phama and
Trang T. T. Quan
*a
aInstitute of Chemistry, Vietnam Academy of Science and Technology, 18 Hoang Quoc Viet, Cau Giay, Hanoi 100000, Vietnam. E-mail: giangnasa86@gmail.com; quanthutrang5986@gmail.com
bGraduate University of Science and Technology, Vietnam Academy of Science and Technology, 18 Hoang Quoc Viet, Cau Giay, Hanoi 100000, Vietnam
cInstitute of Material Science, Vietnam Academy of Science and Technology, 18 Hoang Quoc Viet, Hanoi 100000, Vietnam
First published on 26th August 2025
Hazardous ultraviolet (UV) radiation found in sunlight can seep into food packaging and cause unfavorable physicochemical changes in food items. This study aimed to develop starch-based polymeric biofilms with UV-blocking capability by incorporating CeUiO-66 metal–organic framework nanoparticles (Ce66 NPs). These nanoparticles were synthesized via a solvothermal method using formic acid as a modulator. A Box–Behnken design was used to optimize modulator concentration, reaction temperature, and time to maximize surface area and yield. Under optimal conditions, Ce66 NPs exhibited high crystallinity, an average particle size of 287 nm, a large surface area (832.20 m2 g−1), and a yield of 66.25%. The Ce66 NPs were incorporated into starch films (SCex, x = 0.5–3.0 wt%) via solution casting using glycerol as a plasticizer in an acetic acid medium. Although the addition of Ce66 NPs reduced film transparency, it significantly improved UV-blocking efficiency. Specifically, the SCe1 film blocked 83.5% UVA, 95.6% UVB, and 100% UVC radiation. Water vapor permeability decreased to 1.69 g mm m−2 d−1 kPa−1, and solubility dropped to one third compared to the control film. The tensile strength also increased from 2.2 MPa to 8.4 MPa. Moreover, Ce66 NPs exhibited notable photocatalytic activity, degrading up to 65% of RR195 dye under visible light. This dual functionality underscores the potential of Ce66 NPs for developing multifunctional biofilms for food packaging and environmental treatment.
Nanoparticles such as silver, ZnO, TiO2, CuO, graphene oxide, carbon nanoparticles, and bentonite nanoparticles are considered promising candidates for reinforcing biopolymer films, as they not only enhance characteristics like biocompatibility, tensile strength, Young's modulus, and thermal stability but also improve the light-barrier properties of the resulting films.8,9 Recently, metal–organic frameworks (MOFs) have emerged as materials with high specific surface area, gas barrier properties, good thermal stability, and excellent compatibility with biopolymers, making them suitable additives for developing biofilms with novel functionalities.10–14
Several studies have demonstrated the potential of MOFs in biofilm enhancement. Akash Balakrishnan15 incorporated MOFs into chitosan films for use in food packaging and catalysis. Sanjit Nayak16 employed a zirconium-based MOFs and polycaprolactone (PCL) to create a material capable of controlled release of the herbicide 2-methyl-4-chlorophenoxyacetic acid (MCPA), offering a promising avenue for agricultural applications. Naveed Ahmed Khan10 developed food packaging films by combining ZIF-67 with PVA/starch, and the addition of 4.0 wt% ZIF-67 resulted in a biopolymer film with a mechanical strength of up to 25 MPa and enhanced thermal resistance. L. Sun13 used MIL-125(Ti)-NH2 nanoparticles with cellulose to fabricate biopolymer films with UV shielding capability and a 25.9% increase in mechanical strength. The flame resistance was notably significantly improved, with the limiting oxygen index (LOI) rising from 21.95% to 27.01% in the presence of MIL-125(Ti)-NH2 nanoparticles.
Among MOFs, cerium-based MOFs (Ce-MOFs) are particularly attractive due to their cost-effective synthesis, high chemical and thermal stability, and redox-active Ce3+/Ce4+ sites. These properties make Ce-MOFs suitable for applications in catalysis, corrosion protection, and energy storage.17 Typically, terephthalic acid (H2BDC) and its derivatives are used to synthesize various Ce-MOFs, such as CeUiO-66, with the formula Ce6O4(OH)4(BDC)6, which exhibits high stability and thermal endurance up to 300 °C.18,19 However, the synthesis of nano-sized Ce-MOFs remains challenging, particularly in controlling particle size, porosity, and yield.19 It is well known that synthesis parameters including modulator type and concentration, temperature, and reaction time can profoundly affect the morphology and properties of MOFs.20 During synthesis, carboxylic acids with varying pKa values act as modulators, influencing the size and surface area of the resulting MOFs depending on their dosage.21 Additionally, reaction temperature and time are critical factors affecting crystal formation and growth. Elevated temperatures significantly promote crystal restructuring and Ostwald ripening.22 When the reaction time is prolonged, MOFs crystals tend to evolve into more stable forms with well defined facets under the guidance of facet specific protective agents.23 Further extension of reaction time may induce crystal restructuring and Ostwald recrystallization, potentially affecting the properties of the final MOFs product.22–24
Response Surface Methodology (RSM) is an important technique used to optimize processes. The Box–Behnken Design (BBD), which requires fewer experiments while accurately modeling higher order interactions, has been successfully applied in various fields, including the optimization of film thickness, nanocomposite material synthesis, and mechanical, thermal, and optical property enhancement.25,26
To address these gaps, our study aims to: (1) optimize the solvothermal synthesis of CeUiO-66 nanoparticles (Ce66 NPs) using RSM and BBD to maximize surface area and yield; and (2) incorporate Ce66 NPs into starch based biopolymer films to evaluate their effects on physicomechanical and optical performance. Notably, we demonstrate for the first time the use of Ce66 NPs in enhancing UV-blocking efficiency and mechanical strength of starch films, while also serving as visible light photocatalysts for degradation of the azo dye RR195, a common pollutant in textile wastewater. This dual functionality highlights the potential of Ce66 NPs for both environmental treatment and development of advanced biopackaging materials.
Design Expert software (DXs) was employed to optimize the synthesis process of Ce66 NPs and to identify the most influential synthesis parameters using RSM. The optimized Ce66 NPs were subsequently characterized using XRD, SEM, BET, XPS, TGA, and UV-vis analyses. The physicomechanical properties of the biopolymer film samples containing Ce66 NPs were evaluated through tensile tests, water solubility (WS), water vapor permeability (WVP), transparency, and UV-blocking capability.
To synthesis the biopolymer films, cassava starch (Vietnam, amylose content: 29%, moisture content: 12%) was modified before use. Hydrochloric acid (HCl, 36.5%), sodium hydroxide (NaOH, 98%), sodium bicarbonate (NaHCO3, 99%), acetic acid (CH3COOH, 99.5%), and glycerol (C3H8O3, 99%) were purchased from China.
![]() | (1) |
The opacity (mm−1) was calculated using the formula eqn 2 in the SI.27
The ability to block UVA, UVB, and UVC radiation was determined based on the transmittance values analyzed over the 200–800 nm wavelength range. Specifically, UVA was calculated for the wavelength range of 315–400 nm, UVB for 280–315 nm, UVC for 200–280 nm, and blue light for the wavelength range of 400–495 nm, following the formulas eqn 3 to eqn 6 (SI).1
S = 742.42 − 213.61A − 83.88B + 38.46C + 250.49AB + 78.06AC − 169.97BC − 102.53A2 − 260.49B2 − 244.76C2 | (2) |
H = 62.24 + 2.15A + 15.26B + 5.05C − 0.9650AB − 3.39AC − 3.16BC + 3.87A2 − 22.45B2 − 2.59C2 | (3) |
The selected values presented in eqn (2) and (3) were determined through the analysis of variance (ANOVA) in Table S3, using a significance threshold of P < 0.05. The positive and negative signs of each coefficient indicate the contributing effect of each factor in the model about the H and S of the resulting material. Accordingly, the more positive or more negative the value, the greater its impact, and vice versa.25
For the target function S, all three factors FA, time, and temperature, exhibited a significant influence on the surface area following a second-order model with negative coefficients (−102.53, −260.49, and −244.76, respectively). Notably, FA and temperature, exerted a strong influence on S with a higher positive interaction coefficient (250.49) compared to the interactions of FA/time and temperature/time. Regarding the target function H, both FA and temperature had a strong positive impact on the yield, with second order coefficients of 3.87 and 22.45, respectively. Furthermore, the FA/time and temperature/time interactions also significantly affected the yield. As shown in Table S3, the FA and temperature were the most influential factors on the H. Conversely, for the surface area, temperature and reaction time played the most critical roles.
The influence of various factors on the surface area and the yield in the synthesis of Ce66 NPs is illustrated by three-dimensional (3D) response surface plots (Fig. 1). In these plots, the red zones represent the highest desirable values, while the blue zones indicate lower results. As shown in Fig. 1a, a high concentration of FA acid suppresses the crystallization process, thereby inhibiting particle formation and reducing the surface area during MOFs synthesis.29 The analysis of Fig. 1b confirms that increases in both temperature and time significantly decreases the surface area of the material due to excessive crystal growth of the MOFs. Furthermore, a prolonged time may lead to particle aggregation, resulting in a lower the yield, as illustrated in Fig. 1c. These observations are consistent with the findings reported by Antonietta Mancuso et al..20 From the analysis of Fig. 1, it is evident that the highest synthesis efficiency is achieved under conditions of low FA, short reaction time, and moderate temperature. The optimal synthesis conditions for gaining a high surface area and the yield of Ce66 NPs were determined using DXs. The optimal point, including FA, temperature, and time values, is listed in Table S4, with a maximum desirability of 0.990. Under these optimized conditions, the resulting surface area reached 832.20 m2 g−1, and the yield was 66.25%, with no significant difference at the 95% confidence level between the predicted and experimental values. These results confirm the success of the applied model in optimizing the synthesis process of Ce66 NPs.
Fig. 2 presents the agreement between experimental and predicted values, along with residual plots, for S and H in 15 runs, confirming model reliability. The data presented in Fig. 2a and c further indicate that the model demonstrates a strong correlation, as the data points are closely aligned along a straight line. The response plots of experimental versus predicted values reveal minimal deviation between the values (Fig. 2b and d). The low coefficient of variation (CV%): 6.05% for S and 3.94% for H indicates the high reliability of the experimental data. The model's adequacy was evaluated through the adjusted R2 and predicted R2 coefficients, with a difference of less than 0.2 indicating the accuracy and significance of the proposed models (Table S5). The adjusted R2 and predicted R2 values for H were 0.9865 and 0.928, respectively. For S, the R2 values reached 0.993 and 0.961, respectively.
![]() | ||
Fig. 2 Experimental versus predicted values and random distribution plots of the 15 experimental runs for S (a and b) and H (c and d). |
Beside, the distribution of experimental points appears random and follows a normal distribution.25 These findings validate the robustness and strong compatibility of the proposed model with the experimental results, supporting its application in predicting the synthesis of Ce66 NPs with the dual objective of maximizing both surface area and the yield.
![]() | ||
Fig. 3 XRD pattern (a), SEM image and size distribution (b and c), Ce3d XPS spectrum (d) of Ce66 NPs synthesized under optimal conditions. |
Fig. 3b and c display the Ce66 NPs SEM picture and particle size distribution, which demonstrate that the particles have a quasi-cubic nanostructure with an average size of 287.63 nm. While some degree of agglomeration was observed, forming secondary structures >600 nm, the uniformity of primary particles suggests effective control over crystal growth. This morphology is advantageous in polymer composite applications, where well-defined nanoscale geometry can contribute to better particle dispersion, mechanical reinforcement, and interfacial adhesion within the matrix.
Fig. 3d shows the XPS analysis of Ce66 NPs, revealing characteristic peaks at 903.4 eV (Ce3d3/2) and 884.8 eV (Ce3d5/2) corresponding to Ce3+, along with four additional peaks attributed to Ce4+ species. The Ce3+/Ce4+ ratio was calculated according to the method reported by Xinyu Wu et al.,33 and found to be 46/54 (%). The coexistence of Ce3+ and Ce4+ facilitates electron transfer, thereby enhancing the redox capability of Ce66 NPs, making them promising candidates for photocatalytic degradation of persistent organic pollutants.34 The BET isotherm of Ce66 NPs shows type I behavior, with a high specific surface area of 832.20 m2 g−1 and a total pore volume of 0.49 cm3 g−1 (Fig. S1). In comparison to previously published materials, these better surface features demonstrate how well formic acid (FA) works as a modulator to promote controlled nucleation and inhibit aggregation during the synthesis of Ce66 NP.
Biopolymer film | Tensile strength (MPa) | Elongation at break (%) | Film thickness (mm) |
---|---|---|---|
SCe0 | 2.2 ± 0.2 | 48.3 ± 4.3 | 0.098 ± 0.002 |
SCe05 | 3.2 ± 0.4 | 44.5 ± 4.1 | 0.102 ± 0.006 |
SCe1 | 8.4 ± 0.8 | 47.8 ± 2.3 | 0.101 ± 0.003 |
SCe3 | 15.5 ± 0.7 | 13.5 ± 6.8 | 0.107 ± 0.005 |
Table 1 demonstrates a clear trend of increasing tensile strength and decreasing elongation at break in nanocomposite films with the increasing content of Ce66 NPs. This mechanical behavior is closely linked to both chemical interactions and physical reinforcement mechanisms provided by the Ce66 NPs. The improvement in tensile strength can be attributed to strong interfacial interactions particularly hydrogen bonding and possible coordination bonding between the abundant hydroxyl groups of the starch matrix and the functional groups (carboxylate, hydroxyl) on the Ce66 NPs. The formation of interfacial chemical linkages such as Ce–O–C or Ce–OH–C bridges reinforces the molecular network, resulting in better load transfer efficiency and a stiffer polymer nanoparticle composite. These interactions restrict the mobility of the polymer chains, thus increasing the film's stiffness and mechanical integrity. Additionally, the partially unsaturated 4f orbitals of Ce ions can form coordination complexes with oxygenated groups in the polymer matrix, further contributing to the film's cohesive energy density.36 However, at higher concentrations (SCe3), the nanoparticles tend to aggregate, creating localized stress points and microstructural inhomogeneities that hinder flexibility and reduce elongation at break.37 These findings confirm that Ce66 NPs act as anti plasticizing agents in the film matrix, which also leads to a slight increase in the overall thickness of the nanocomposite films as the nanoparticle content increases.
However, at higher nanoparticle concentrations, the surface structure becomes rough, with visible cracks and noticeable agglomeration of Ce66 NPs into clusters (Fig. 5d). This aggregation is thought to be caused by the high surface energy of the nanoparticles, which promotes clustering within the polymer matrix.39 This phenomenon was also confirmed by Iman Shahabi-Ghahfarrokhi in his study.40
The second weight loss stage occurs between 175 °C and 450 °C, corresponding to the glycerol decomposition (190–250 °C) and the degradation of starch molecules. Notably, the biopolymer films exhibited lower weight loss than the neat starch film in this stage, likely due to the breakdown of polymer chains and residual solvents confined within the MOFs nanopores.42 The incorporation of Ce66 NPs into the biopolymer films acts as a physical barrier and nanofiller that resists structural chain scission caused by thermal stress, thereby retarding the thermal degradation process.14
In the third stage (T > 450 °C), thermal cracking of the polymer chains occurs, leading to the formation of carbonaceous species and ash residues. The higher ash content in the biopolymer films compared to the pure starch film can be attributed to the catalytic role of Ce-MOFs in the cracking process, which facilitates the generation of residual carbon.43,44 These TGA results confirm that Ce66 NPs serve as a protective barrier, enhancing the thermal stability of the biopolymer films.
The XRD patterns of SCex films is presented in Fig. 6b. The XRD pattern of the starch film without Ce66 NPs exhibits broad, low intensity diffraction peaks and a strong amorphous halo, characteristic of semicrystalline polymer materials with low crystallinity. Diffraction peaks at 2θ 17–26° correspond to type B starch crystallinity, indicating interactions between amylose and amylopectin following the gelatinization process.14
At Ce66 NPs concentrations below 0.5% wt, the characteristic peaks of Ce66 NPs are almost unobservable due to their high dispersion within the polymer matrix. However, when the Ce66 NPs content increases to 1.0%, the diffraction peaks between 2θ 7–8.5°, typical of the Ce-UiO-66 crystalline structure, reappear.32 The strong diffraction signals observed in the SCe3 sample indicate a substantial aggregation of Ce66 NPs crystals within the polymer matrix, consistent with the SEM observations.
The WVP refers to the amount of water vapor passing through the biopolymer films. High WVP is generally undesirable for preserving moisture sensitive products such as pharmaceuticals or dried goods. As seen in Fig. 7b, it can be seen that the pristine starch film exhibited a high WVP value of 2.84 g mm m−2 d−1 kPa−1, which is attributed to the presence of hydrophilic plasticizers such as glycerol acting as hydrocolloids that enhance water vapor permeability.47 Upon the incorporation of Ce66 NPs, the WVP decreased and reached 2.25 (SCe05), 1.69 (SCe1), and 1.81 g mm m−2 d−1 kPa−1 (SCe3), respectively. The observed increase in WVP between SCe3 and SCe1 is attributed to the excessive presence of porous nanoparticles, which disrupted the dense film structure and accelerated water molecule penetration through capillary channels within the polymer matrix.27 The nanoparticles acted as hydrophobic agents, increasing the tortuous pathway for water diffusion and thereby reducing WVP. Similar observations have also been reported in previous studies.48,49
Fig. 8b illustrates the influence of Ce66 NPs concentration on the UV-blocking capabilities of the biopolymer films, particularly for UVA, UVB, UVC, and blue light. The SCex films demonstrated complete (100%) blocking of UVC radiation. The SCe0 film blocked 61.25% of UVA and 35.65% of UVB, and 30.5% of blue light, respectively. These values improved with the inclusion of Ce66 NPs at varying concentrations. Specifically, UVA blocking efficiency increased from 83.5% to 100% in SCe05, SCe1, and SCe3. UVB shielding also improved, reaching 68.12% and 95.6% in SCe05 and SCe1, respectively. Notably, the SCe3 film blocked both UVB and blue light at 100% and 97.2%, respectively.
However, SCe3 exhibited a high opacity of 16.50 mm−1, along with nanoparticle aggregation and membrane fracture, as observed in SEM images, significant reducing in elongation percentage. Therefore, it is unsuitable for food packaging applications. The UV-blocking mechanism is associated with the light absorption properties and the Ebg of Ce66 NPs, as demonstrated in Fig. 4. Upon light absorption, Ce66 NPs trap the light and generate photoexcited electrons and holes at higher energy states, thereby reducing the amount of UV radiation reaching the SCex films.1
In general, films lacking UV-blocking capabilities may accelerate oxidative degradation, leading to nutrient loss in preserved food and negatively affecting the stability of organic materials (e.g., discoloration and degradation).51 Therefore, the SCex films, exhibiting excellent UV-blocking performance, show great potential for protective applications in food packaging and optoelectronic devices. Comparative evaluations with previously reported packaging films are summarized in Table 2.
Reinforced nanomaterials | Biopolymers or polymers | Mechanical properties | UV-blocking | WVP | Enhanced functionalities | References | |
---|---|---|---|---|---|---|---|
Tensile strength | Elongation at break | ||||||
Silver nanoparticle | Cassava starch | 4.2 MPa | 4.7% | Not specified | Not specified | Non-toxicity to fibroblast cells | 52 |
ZnO | Starch/agar | 5.331 MPa to 7.459 MPa | 32.178 to 55.771% | 63.1% to 67.78% UVA | Not specified | 53 | |
74.5% to 81% UVB | |||||||
Halloysite nanotube | Starch | 3.5 MPa to 5.73 MPa | 25 to 40% | Not specified | 1.89 to 3.07 g mm m−2 d−1 kPa−1 | Excellent flame retardancy | 54 |
Graphite oxide carbon | Starch | 2.1 Mpa to 21.7 Mpa | 45.73 to 59.87% | Not specified | 3.86 to 3.27 g mm m−2 s−1 kPa−1 | 55 | |
NH2-UiO-66 | Corn starch, gellan gum | 28.5 MPa to 31.8 MPa | 25% to 16% | Not specified | 2.98 g mm m−2 d−1 kPa−1 | Antibacterial | 39 |
Ce66 NPs | Starch | 2.2 MPa to 8.4 MPa | 47.8 to 48.3% | 83.5% UVA | 1.69 g mm m−2 d−1 kPa−1 | Ce-UiO-66 was capable of degrading 65% of RR195 dye | This work |
95.6% UVB | |||||||
100% UVC |
Among the nanocomposite films containing nanoparticles summarized in Table 2, the starch-based biofilm incorporating Ce66 NPs demonstrates a unique combination of enhanced UV-blocking and excellent water vapor permeability properties, making it a highly promising material for food packaging applications. Compared to other nanofillers, the SCe1 film achieved superior UV-blocking performance, effectively shielding 83.5% of UVA, 95.6% of UVB, and 100% of UVC radiation significantly outperforming ZnO-based films, which reached a maximum UVB shielding efficiency of 81%. In terms of WVP characteristics, the SCe1 film exhibited one of the lowest WVP values (1.69 g mm m−2 d−1 kPa−1), surpassing even halloysite nanotube and graphite oxide based composites, which are known for their barrier performance. According to the Chinese standard (BB/T 0041-2021), the acceptable WVP value for packaging materials is less than 6.0 g (m2 24 h)−1. The WVP of the film obtained in the present study was 1.69 g mm m−2 d−1 kPa−1, which corresponds to 40.14 g (m2 24 h)−1, a relatively high value. However, the WVP of the film developed in this study was found to be better than that of several previously reported biopolymer-based films.56 Furthermore, the tensile strength of the SCe1 film increased markedly from 2.2 MPa to 8.4 MPa, indicating strong reinforcement while still maintaining appropriate flexibility.
Beyond its use as a reinforcing nanofiller, Ce66 NPs also demonstrated independent photocatalytic activity, which allowed them to degrade up to 65% of the reactive dye RR195 in the presence of sunlight (Fig. S3 to S5). This multifunctionality, along with the enhanced UV resistance and water barrier properties, highlights the considerable potential of Ce66 NPs for advanced food packaging solutions.
Ce66 NPs not only enhanced the removal efficiency in degrading RR195 dye under sunlight (65%) but also significantly improved the physicomechanical properties of starch based biopolymer films. Specifically, the SCe1 film demonstrated outstanding UV-blocking capability, blocking 83.5%, 95.6%, and 100% of UVA, UVB, and UVC radiation, respectively far superior to starch films without nanoparticles. Regarding of mechanical properties, the tensile strength of the films increased from 2.2 MPa (SCe0) to 15.5 MPa (SCe3), indicating substantial reinforcement due to the incorporation of Ce66 NPs. Furthermore, the water solubility of the films was reduced threefold, and the water vapor absorption capacity decreased to 1.69 g mm m−2 d−1 kPa−1, which corresponds to 40.14 g (m2 24 h)−1, demonstrating improved stability in humid environments for the SCex films containing Ce66 NPs.
These findings confirm the dual functional potential of Ce66 NPs as efficient photocatalysts for environmental pollutant treatment and as ideal nanofillers to enhance the mechanical and UV-blocking properties of biopolymer films thus opening new avenues for developing environmentally friendly food packaging materials.
Supplementary information is available. See DOI: https://doi.org/10.1039/d5ra03117f.
This journal is © The Royal Society of Chemistry 2025 |