Literature DB >> 35721923

Functionalization and Modification of Polyethylene Terephthalate Polymer by AgCl Nanoparticles under Ultrasound Irradiation as Bactericidal.

Mitra Alidadykhah1, Hossein Peyman1, Hamideh Roshanfekr1, Shohreh Azizi2,3, Malik Maaza2,3.   

Abstract

Polyethylene terephthalate polymer (PET) is widely used in diverse areas. In the current study, the surface of PET is modified in two steps in order to improve the quality. At first, the polymer was functionalized with carboxylic groups, and Fourier transform infrared spectroscopy studies were used to verify functionalization. Then, AgCl nanoparticles were synthesized on COOH functional groups on the surface of PET using a sonochemistry method by sequential dipping of the functionalized polymer in an alternating bath of potassium chloride and silver nitrate under ultrasonic irradiation. The effects of ultrasonic irradiation power, the number of dipping steps, and pH on the growth of AgCl nanoparticles as effective parameters on size and density of synthesized Ag nanoparticles were studied. The results of scanning electron microscopy studies showed that the size and density of AgCl nanoparticles under ultrasonic irradiation with a power of 100 W are better than those of AgCl nanoparticles under irradiation with a power of 30 W. Also, by 15 times dipping the polymer into the reagent solutions in pH = 9, the modified polymer with a greater number of nanoparticles with suitable size can be reached. Antibacterial properties of PET containing AgCl nanoparticles were investigated against six Gram-positive and Gram-negative bacteria species, and the results showed significant antibacterial activity, while functionalized PET did not have a significant effect on both types of bacteria.
© 2022 The Authors. Published by American Chemical Society.

Entities:  

Year:  2022        PMID: 35721923      PMCID: PMC9202035          DOI: 10.1021/acsomega.1c07082

Source DB:  PubMed          Journal:  ACS Omega        ISSN: 2470-1343


Introduction

Polyethylene terephthalate (PET) is a linear and aromatic polyester that is the production of reaction between terephthalic acid and ethylene glycol.[1,2] PET composites have a wide range of industrial applications, including in packaging, construction, automotive parts, electronic equipment, and the textile industry.[3] Also, this polymer is widely used in medical applications such as vascular prostheses,[4,5] heart valve sewing cuffs,[6,7] implantable sutures,[8] and other surgical usage.[9−12] As an inert polymer with no surface reactive functional groups, modification of the PET surface can improve its hemocompatibility. Therefore, by surface functionalization, nanoparticles can be immobilized on the surface, and it subsequently could improve the desirable properties of PET. In the recent years, hydrolysis, reduction, glycolysis, aminolysis, amination,[9−11,13−16] and the other various techniques have been applied to introduce reactive functional groups on PET surfaces.[17] Carboxylation is another technique which introduces carboxylic groups on the PET surface without any change in bulk and surface properties. Therefore, in this study, the PET surface is modified with carboxylation in order to improve the surface properties and stabilize nanomolecules on it. Currently, due to specific properties, nanoparticles are widely produced and used in industrial areas.[18] Properties of mineral nanoparticles depend on their size and morphology. Controlled design and synthesis of nanoparticles in different size and morphology are very important in both scientific and technological fields.[19−21] In this context, nano-crystalline silver halide coatings on some substrates with large surface areas have received major interest in recent years. Desirable optical, magnetic, catalytic, and antibacterial properties of AgCl make it a good candidate in different areas such as the photography, pharmaceutical, and electronic industry.[22,23] Various techniques have been developed for preparing AgCl nanoparticles such as electrospinning,[24] template synthesis,[25] microemulsion,[4,26−28] reverse micelles,[29] laser-based synthesis,[30] host–guest nanocomposite material,[31,32] ultrasonic spray pyrolysis,[33] and sonochemistry.[34] In the current study, the sonochemistry method is applied to synthesize AgCl nanoparticles on the surface of functionalized PET. Recently, the effects of ultrasonic irradiation on the chemical reactions have been reported in various studies.[35] In this method, molecules undergo chemical changes under powerful ultrasonic irradiation.[36−38] All products of sonochemical reactions are in nanoscale with variety in size, shape, structure, and solid phase (amorphous or crystalline).[39] One of the advantages of ultrasonic irradiation is that there is no need of a surfactant and high temperature;[40−43] also, it yields nanoparticles in smaller size.[40,44,45] Ultrasonic irradiation accelerates chemical reactions, and those reactions that are hardly possible under normal conditions can be carried out under ultrasonic irradiation.[46,47] In this study, PET fibers were carboxylated and coated with AgCl nanoparticles using ultrasonic irradiation for the first time. The growth of AgCl nanoparticles on the functionalized PET fibers was reached by sequential dipping steps in an alternating bath of potassium chloride and silver nitrate.[48]

Results and Discussion

Mechanism and Characterization of −COOH Functionalization

PET functionalization was carried out in two steps: First, in the presence of acetic acid and formaldehyde solution, the −CH2OH group bonded to the aromatic ring. In the second step, in the presence of sodium hydroxide and bromoacetic acid solution, the −CH2OH group became deprotonated and changed into the carboxylic acid group. The mechanism is that formaldehyde captures a proton and becomes +CH2OH under acidic conditions. In the presence of PET, protonated formaldehyde acts as an electrophile molecule and attacks one of the double bonds in the aromatic ring via its positively charged carbon, and it leads to the formation of a transition-state intermediate. By adding NaOH, OH– removes one of the hydrogens near formaldehyde on the aromatic ring (in the form of H2O) leading to the formation of a stable product with the −CH2OH substituent on the aromatic ring. In an alkaline pH, the CH2OH substituent loses its alcoholic proton in the presence of bromoacetic acid, and then, CH2O– attacks the carbon which is bonded to bromine in bromoacetic acid via a nucleophilic mechanism, and by removing the bromide ion, the CH2OCH2COO– substituent will be produced on the surface of PET (Figure ).[8]
Figure 1

PET functionalized mechanism.

PET functionalized mechanism. As shown in Figure , spectrum A is related to a non-functionalized PET polymer, and spectrum B is related to a functionalized PET polymer in which the −COOH functional group is located on its surface.
Figure 2

FT-IR spectrum of PET, (A) non-functionalized PET and (B) functionalized PET by acetic acid groups.

FT-IR spectrum of PET, (A) non-functionalized PET and (B) functionalized PET by acetic acid groups. In spectrum A, stretching vibrations of O–H at the end of the PET polymer (34334.69 cm–1), esteric C=O groups (1626.68 cm–1), C–O group (1038.09 and 1107.81 cm–1), C=C group of aromatic rings (1457.54 cm–1), CH2–CH2 group (2858.03 and 2924/57 cm–1), and out of plane C–H (802.29 cm–1) are shown. Generally, the stretching vibration of the esteric C=O group is located at 1735–1750 cm –1, but here, due to being near the aromatic ring, it acts as an electron-withdrawing group and conjugates with the aromatic ring that leads to reduced frequency and energy; therefore, the absorption peak of esteric C=O appears in lower frequency. The C=C group has a double stretching vibration peak (1475 and 1600 cm–1), but due to being near the esteric C=O group, there is an overlapping in the spectra peak at 1600 cm–1; therefore, it appears in 1457.54 cm–1. In spectrum B, there are peaks related to the functional groups of the PET polymer and −COOH functional group. Stretching vibration of O–H at the end of the polymer (3436 cm–1), acidic O–H (3070 cm–1), polymeric C=O (1633 cm–1), and acidic C=O (1731 cm–1) is shown in spectrum B. Basically, the stretching vibration frequency of acidic C=O should be lower than that of esteric C=O (1700–1730 and 1735–1750 cm–1, respectively), but due to the withdrawing substituent in the aromatic ring, the frequency of C=O shifted to a frequency lower than that of acidic C=O. Stretching vibration frequencies of polymeric C–O, acidic C–O, and polymeric C=C are 1030 and 1095, 1455, and 1508 and 1582 cm–1, respectively, and stretching vibration of out of plane C–H is at 799 and 873 cm–1. Those stretching vibration peaks related to out of plane C–H indicate the types of substituents in the aromatic ring, and the two C=O substituents are in the para position.

Mechanism of AgCl Nanoparticle Synthesis

In alkaline pH, the surface of the polymer is negatively charged because carboxylic groups are deprotonated.[40,48] By dipping the negatively charged polymer in AgNO3 solution, Ag+ ions will attach to the PET surfaces via an electrostatic bond and electron-rich atoms in the carboxylic group, and the other groups of polymers interact with the electropositive metal cations. After the dipping step in AgNO3 solution, rinsing the polymer will wash out those cations which are weakly attached to the other sites rather than carboxylic groups. By dipping the polymer into the KCl solution, the formation of AgCl nanoparticles is initiated. By repeating the sequential dipping steps in the alternating bath, AgNO3 and KCl solutions cause the growth of AgCl nanoparticles and increase their number and density.

Ultrasound Effects

In order to study the effect of ultrasonic irradiation on the characteristic of produced nanoparticles, the control samples were treated without ultrasonic irradiation, in which AgCl nanoparticles reached on the surfaces of the PET polymer by sequential dipping steps in the alternating bath with no ultrasonic irradiation.[34] The product was dried and studied by scanning electron microscopy (SEM). The results show that the average size of AgCl nanoparticles is in the range of 78.33 nm (Figure ). The average size of AgNO3 nanoparticles with the same sequential dipping steps and applying different ultrasonic irradiations is 65.51 and 62.33 nm for lower power (30 W) and higher power (100 W), respectively (Figures –7). Ultrasonic irradiation has two primary effects on a liquid: cavitation (formation, growth, and collapse of bubbles) and heating. When the bubbles collapse near the surface of a solid substrate, they make powerful, turbulent, and microjet waves that lead to the effective mixing in the layers of liquid. The impact of cavitation in non-homogenized systems is several hundred times more than that of homogenized systems.[49] Also, ultrasonic irradiation promotes the rapid migration of new nanoparticles to the surface of PET; therefore, in the presence of ultrasonic irradiation, there is no need of high temperature during the reaction, and the size of nanoparticles is smaller.[31,50] Also, as shown in Figures –7, applying high-power ultrasonic irradiation causes the smaller size of nanoparticles.
Figure 5

SEM of the blank sample (without ultrasound irradiation). 15 sequential dipping steps and pH = 9.

Figure 6

SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 30 W, and pH = 9.

Figure 7

SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 9.

FT-IR spectrum of PET modified by AgCl-NPs. XRD spectrum of PET modified by AgCl-NPs. SEM of the blank sample (without ultrasound irradiation). 15 sequential dipping steps and pH = 9. SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 30 W, and pH = 9. SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 9.

pH Effect

The AgCl nanoparticles are synthesized in different pH: 5, 7, 9, and 11. According to the results (Figures -11), the average diameters of nanoparticles in pH 5, 7, 9, and 11 are 94.65, 70.77, 62.33, and 84.39 nm, respectively.
Figure 8

SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 5.

Figure 11

SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 11.

SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 5. SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 7. SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 9. SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 11. It can be concluded that the size of AgCl nanoparticles is reduced by increasing pH to 9, but in pH higher than 9, that is, pH 11, the AgCl nanoparticle size is increased, but the density of nanoparticles is decreased. The reason is that in higher pH, the opportunity of AgOH formation is more than that of the AgCl nanoparticle formation, and due to formation of AgOH sediments, the size of other nanoparticles will be increased.

Effects of Sequential Dipping Steps

In the synthesis of AgCl nanoparticles, to reach the optimum number of dipping steps in the reagent solutions, the reactions were carried out with three different numbers of dipping steps: 10, 15, and 20 times in pH = 9 and under the same condition. The results of SEM studies show that the average diameter of AgCl nanoparticles with a dipping step of 10, 15, and 20 times is 59.57, 62.33, and 62.75 nm, respectively (Figures –14). It can be concluded that by increasing the number of sequential dipping steps in AgNO3 and KCl solutions, the time of reaction will be increased, and this leads to the increased growth, size, and number of AgCl nanoparticles.
Figure 12

SEM of AgCl-NP synthesis on the PET fiber. 10 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 9.

Figure 14

SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 20.

SEM of AgCl-NP synthesis on the PET fiber. 10 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 9. SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 9. SEM of AgCl-NP synthesis on the PET fiber. 15 sequential dipping steps, ultrasound irradiation power 100 W, and pH = 20. The optimum number of dipping steps should lead to the lowest diameter (smallest size) and highest density of nanoparticles. By increasing the number of sequential dipping steps in the reagent solutions, the size of nanoparticles will increase, but as shown in the figures, in the samples that were sequentially dipped 15 times in the reagent solutions, the nanoparticle size is smaller than the size of those dipped 20 times in the reagent solutions. In the synthesis of nanoparticles, not just the size but also the density of nanoparticles is important. In cycle 10 (dipping 10 times in the solutions), due to the lower number of nanoparticles, the density will be low too. However, in the higher cycles, the higher density of nanoparticles leads to higher distribution of size; therefore, cycle 15 was regarded as an optimum number of dipping steps. Summary results are shown in Table .
Table 1

Optimized Conditions of AgCl-NP Synthesis on Carboxylate PET

ultrasound effectsa
without ultrasoundhigh-power ultrasoundlow-power ultrasound
78.33 nm62.33 nm65.51 nm

Other conditions: pH = 9, sequential dipping steps = 15.

Other conditions: ultrasound power = 100 W, sequential dipping steps = 15.

Other conditions: pH = 9, ultrasound power = 100 W.

Other conditions: pH = 9, sequential dipping steps = 15. Other conditions: ultrasound power = 100 W, sequential dipping steps = 15. Other conditions: pH = 9, ultrasound power = 100 W.

Bactericidal Tests

To investigate the antibacterial effect of AgCl nanoparticles on the surface of the PET polymer against two bacterial species, the modified PET polymer was added to the bacterial growth medium; after 18–24 h incubation, the results show no bacterial-growth zone due to the antibacterial properties of the modified PET polymer with AgCl nanoparticles (Figure ). AgCl nanoparticles synthetized on the PET surface showed the highest antibacterial activity against Staphylococcus aurous (ATCC 43300) and Bacillus subtilis (ATCC 6633).[2,15,51]
Figure 15

Pictures of the bactericidal test, (A) Staphylococcus aurous and (B) Bacillus subtilis by functionalized PET (PET-COOH), non-functionalized PET (PET), AgCl nanoparticles synthesized in pH 11 (PET-AgCl-NPs 1), AgCl nanoparticles synthesized in pH 9 and low power (PET-AgCl-NPs 2), and AgCl nanoparticles synthesized in pH 9 and high power (PET-AgCl-NPs 3).

Pictures of the bactericidal test, (A) Staphylococcus aurous and (B) Bacillus subtilis by functionalized PET (PET-COOH), non-functionalized PET (PET), AgCl nanoparticles synthesized in pH 11 (PET-AgCl-NPs 1), AgCl nanoparticles synthesized in pH 9 and low power (PET-AgCl-NPs 2), and AgCl nanoparticles synthesized in pH 9 and high power (PET-AgCl-NPs 3).

Conclusions

PET was functionalized in two steps, and Fourier transform infrared spectroscopy (FT-IR) studies were performed to confirm the functionalization and the possible presence of carboxylic groups on the surface of the polymer. PET coated with AgCl nanoparticles was obtained by sequential dipping steps under ultrasonic irradiation. The effects of ultrasonic irradiation, sequential dipping steps, and pH on the growth of AgCl nanoparticles were studied. SEM images verify the synthesis of AgCl nanoparticles on the surface of the PET polymer. Antibacterial activity of the modified surface was studied against two Gram-positive and Gram-negative bacterial species. The results showed that in a power of 100 W, pH = 9, and cycle 15 (dipping 15 times in the solutions), AgCl nanoparticles can be synthesized with an average size of 62.33 nm and the maximum density on the surface of the functionalized polymer with the carboxylic group.

Experimental Section

Materials

PET fibers were supplied by Pouya Nakh Ilam Co. All the reagents and solvents were purchased from Merck chemical company and used without further purification. To investigate the functionalization of PET, FT-IR (Vertex70) studies were used. SEM (Philip’s Company, Netherlands) was applied to verify the synthesis of AgCl nanoparticles on the surface of PET. All the reactions were performed under different ultrasound irradiation powers (30 and 100 W) using Elmasonic P60H.

Methods

Functionalization of PET

1 g of PET was rinsed with distilled water and ethanol and then dried for 3–4 h in an oven at 55 °C. PET functionalization was carried out in two steps: First, PET fibers were immersed in a solution of formaldehyde 18.5% and acetic acid 1 M for 4 h in room temperature. In the second step, PET was immersed in a solution of bromoacetic acid 1 M and NaOH 2 M for 18 h; then, it was rinsed with distilled water two times (for 15 min) and dried in an oven for 48 h at 55 °C. The functionalized PET was characterized using FT-IR in order to verify the functionalization.[8,52] Figure shows the synthesis of AgCl nanoparticles on the surface of PET; at the wavenumber lower than 800 cm–1, peaks are formed, indicating the formation of nanoparticles on the surface of the PET and the creation of strong bonds between the metal and the surface of the polymer.[20]
Figure 3

FT-IR spectrum of PET modified by AgCl-NPs.

Based on Figure of the XRD pattern mentioned below, the Miller indices at levels (111), (200), (220), and (311) correspond to the angles of 38.143, 25.465, 51.64, and 77.011°, respectively, which confirms the presence of silver nanoparticles on the surface of the modified PET polymer. The additional peaks are related to the impurities in the PET polymer. Based on the studies performed and according to the crystalline plates expressed, it was found that silver is crystallized in the structure of an FCC (cubic centers of total funds).
Figure 4

XRD spectrum of PET modified by AgCl-NPs.

Coating of PET with AgCl Nanoparticles

The growth of AgCl nanoparticles on the surfaces of carboxylated PET fibers was reached by sequential dipping steps in an alternating bath of potassium chloride and silver nitrate under ultrasound irradiation (frequency was constant 80 kHz for 20 min). At first, the carboxylated PET polymer was placed in water, and the pH of this solution was adjusted to pH 9 with diluted potassium hydroxide. Then, sequential dipping of functionalized PET in AgNO3 and KCl solutions was done. After bringing out the PET fibers from AgNO3 solution, PET was washed in order to remove unattached ions. Dipping PET in KCl solution was followed by AgCl complex formation and initiation of AgCl nanoparticle formation. Repeating the sequential dipping steps in the alternating bath led to AgCl nanoparticle growth (Figure ).
Figure 16

Scheme of the AgCl-NP synthesis mechanism on the PET fiber.

Scheme of the AgCl-NP synthesis mechanism on the PET fiber. The duration time of the dipping step for each solution was 1 min followed by a 1 min washing step.[48] At the end of the modification process, the samples were dried for 24 h in an oven at 55 °C. In order to study the effect of ultrasonic irradiation on the synthesis and size of nanoparticles, all the experiments were performed in a power of 30 and 100 W. To investigate the influence of pH on AgCl nanoparticle synthesis, solutions were prepared in a pH range of 5–11. All steps of AgCl nanoparticle formation were carried out on the surface of PET in different numbers of dipping steps to reach an optimum number of dipping cycles.[53] After preparing nutrient Muller-Hinton agar medium in the plates, 4 mm diameter wells were made in the medium using a Pasteur pipette (well diffusion method). Next, certain amounts of modified PET coatings with different amounts of AgCl nanoparticles, functionalized and non-functionalized PET, were put in the wells of plates (weight-wise). In the next step, two different bacterial species were added to the wells separately followed by incubation for 18–24 h to study the inhibition growth zone as an indicator of antibacterial activity of modified PET with AgCl nanoparticles against these two different bacterial species: Staphylococcus aurous (ATCC 43300) and B. subtilis (ATCC 6633).
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