Next Article in Journal
A Study on the Thermal Degradation of an Acrylamide and 2-Acrylamido-2-Methylpropanesulfonic Acid Copolymer at High Temperatures
Next Article in Special Issue
Mechanistic Insights into Anion-Induced Electrochromism of Ru(II)-Based Metallo-Supramolecular Polymer
Previous Article in Journal
The Reliability of PCL/Anti-VEGF Electrospun Scaffolds to Support Limbal Stem Cells for Corneal Repair
Previous Article in Special Issue
Developing Transparent and Conductive PolyHEMA Gels Using Deep Eutectic Solvents
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Polymers
Volume 15
Issue 12
10.3390/polym15122664
polymers-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

In Situ Redox Synthesis of Highly Stable Au/Electroactive Polyimide Composite and Its Application on 4-Nitrophenol Reduction

by
Yi-Sheng Chen
1,
Wei-Zhong Shi
1,
Kun-Hao Luo
2,
Jui-Ming Yeh
2,* and
Mei-Hui Tsai
1,3,*
1
Department of Chemical and Materials Engineering, National Chin-Yi University of Technology, Taichung 411030, Taiwan
2
Department of Chemistry, Chung Yuan Christian University, Chung Li District‚ Tao-Yuan City 32023, Taiwan
3
Graduate Institute of Precision Manufacturing, National Chin-Yi University of Technology, Taichung 411030, Taiwan
*
Authors to whom correspondence should be addressed.
Polymers 2023, 15(12), 2664; https://doi.org/10.3390/polym15122664
Submission received: 13 May 2023 / Revised: 31 May 2023 / Accepted: 2 June 2023 / Published: 13 June 2023
(This article belongs to the Special Issue Synthesis, Characterization and Applications of Electroactive Polymers: 2nd Edition)
Browse Figures
Review Reports Versions Notes

Abstract

:
In this study, we developed a series of Au/electroactive polyimide (Au/EPI-5) composite for the reduction of 4-nitrophenol (4-NP) to 4-aminophenol (4-AP) using NaBH4 as a reducing agent at room temperature. The electroactive polyimide (EPI-5) synthesis was performed by chemical imidization of its 4,4′-(4.4′-isopropylidene-diphenoxy) bis (phthalic anhydride) (BSAA) and amino-capped aniline pentamer (ACAP). In addition, prepare different concentrations of Au ions through the in-situ redox reaction of EPI-5 to obtain Au nanoparticles (AuNPs) and anchored on the surface of EPI-5 to form series of Au/EPI-5 composite. Using SEM and HR-TEM confirm the particle size (23–113 nm) of the reduced AuNPs increases with the increase of the concentration. Based on CV studies, the redox capability of as-prepared electroactive materials was found to show an increase trend: 1Au/EPI-5 < 3Au/EPI-5 < 5Au/EPI-5. The series of Au/EPI-5 composites showed good stability and catalytic activity for the reaction of 4-NP to 4-AP. Especially, the 5Au/EPI-5 composite shows the highest catalytic activity when applied for the reduction of 4-NP to 4-AP within 17 min. The rate constant and kinetic activity energy were calculated to be 1.1 × 10−3 s−1 and 38.9 kJ/mol, respectively. Following a reusability test repeated 10 times, the 5Au/EPI-5 composite maintained a conversion rate higher than 95%. Finally, this study elaborates the mechanism of the catalytic reduction of 4-NP to 4-AP.

Graphical Abstract

1. Introduction

The rise of industrial civilization has led to the improvement of people’s living standards, but also has led to environmental and human health problems. Among the many water pollutants, 4-nitrophenol (4-NP) is a simple organic aromatic compound that is widely used in dyes, pesticides, and pharmaceuticals [1]. Because of the improper discharge of industries in modern society, 4-NP has become a common pollutant in soil and groundwater. It is worrying that 4-NP is easily dissolved in water and has carcinogenic properties, and many reports have shown that inadvertent ingestion or entry into the human body through the respiratory tract can cause nausea, headache, and eye irritation [2]. In fact, this is one of the reasons why the U.S. Environmental Protection Agency (USEPA) has identified 4-NP and its derivatives as the top priority pollutants for removal [3]. 4-NP is used in various forms in agriculture and other industrial environments, and effective removal and detection of 4-NP is essential due to its adverse effects on humans and the environment.
Several methods of 4-NP removal have been reported in the literature. These methods contain adsorption [4], photocatalytic degradation [5], microbial decomposition [6,7], Fenton [8], peroxymonosulfate [9], and solid phase extraction [10]. Unfortunately, these methods require stringent operating conditions and time-consuming processing, thus increasing the economic demand and possibly causing secondary pollution problems to the environment. So far, catalytic reduction has been considered by many researchers as a relatively green and economical technique for the decomposition and removal of pollutants under mild conditions. The conversion of 4-NP to the less toxic 4-aminophenol (4-AP) by sodium borohydride (NaBH4) as a hydrogen source was evaluated as a basic reaction model in aqueous media [11] and easily monitored with high accuracy by UV-Vis spectroscopy. 4-AP is an environmentally friendly and important intermediate for the preparation of many economic products, such as dyes manufacturing [12], photographic developers [13], antipyretic drugs [14], and corrosion inhibitors [15]. However, the catalytic reduction of 4-NP is very difficult and time-consuming in the absence of catalysts due to the need to overcome kinetic barriers [16]. Therefore, the development of highly efficient, environmentally friendly, and reusable catalysts has received close attention from many research groups in recent years.
Noble metal nanoparticles (such as Au, Pt, and Pd) have attracted great interest due to their unique catalytic properties, optical and electronic structures, biocompatibility, and high specific surface area, and they are widely used in biomedicine [17], sensors [18], fuel cells [19], and heterogeneous catalysis [20]. It is worth noting that the remarkable catalytic efficiency of noble metal nanoparticles can be attributed to the highly ordered structure, rapid electron transfer capacity, and large surface area to volume ratio. volume. Although metal/metal oxide nanoparticles exhibit excellent catalytic efficiency, there are limitations in their application to catalysts, such as: (i) their high surface energy and tendency to agglomerate and form larger size nanoparticles, resulting in reduced catalytic performance; and (ii) difficulty in recycling from the reactants to achieve reusability due to their nanometer scale [21]. Tsai et al. [22] prepared the amino-functionalized zirconium phosphate nanosheet decorated with Au nanoparticles composite (Au/ZrP) for the catalytic reduction of 4-NP, and the reaction was completed within 180 s with no significant activity loss through ten consecutive cycles. Das et al. [23] prepared a simple and environmentally friendly method for making a reduced graphene oxide (RGO) nanocomposite decorated with silver nanoparticles (AgNPs) for the reduction of 4-NP to 4-AP within 8 min. These studies showed that loading noble metal nanoparticles onto various carriers (e.g., metal oxides, graphene, polymers, clay, metalorganic frameworks) is an effective way to inhibit their agglomeration and improve the catalytic activity through synergistic effects [24,25].
Since the first introduction of polyacetylene in 1977, conductive polymers (CPs) such as polyaniline, polypyrrole, and polythiophene have received much attention for their environmental stability, low cost, ease of synthesis and special doping/de-doping properties [26]. In recent years, the synergistic effect between polyaniline and noble metal nanoparticles has shown admirable catalytic performance and excellent stability in the field of catalysis [27]. However, polyaniline has poor solubility in common organic solvents, in addition, its electrical conductivity decreases with longer cycle times [28].
To solve these problems, oligoanilines can completely replace polyaniline, which have a similar electronic structure and redox property as polyaniline, and can obtain an ordered molecular structure and good solubility Zheng et al. reported the synthesis and identification of aniline tetramer and aniline pentamer [29]. Qiu et al. developed the synthesis and electrochemical properties of aniline nonamer (Nano-aniline) [30]. In addition, many efforts have been made by researchers to incorporate electroactive aniline oligomers into polymers to form electroactive polymers (EAPs). Wang and Chao et al. reported the development of electroactive polymers containing aniline oligomers on the main and side chains, which were used to study the electrochemical sensing and optical properties of the polymers [31]. Zuo and coworkers synthesized electroactive polyurethane gel containing aniline trimers, which exhibited tunable hydrophilicity, swelling capacity, and biodegradability [32].
On the other hand, electroactive polyimides (EPI) derived from aniline oligomers have excellent mechanical strength, thermal stability, and reversible redox behavior of polyimide. Yeh et al. have published many related studies, such as anticorrosive materials [33], chemical sensors [34], gas separation films [35], and electrochromic [36]. In recent years, electroactive polymers or conductive polymers have been developed and used as promising catalyst carriers. The high specific surface area and microporosity not only confine the growth of metallic nanoparticles, but also highly dispersion compared to conventional catalyst carriers (e.g., graphene, metal oxide) [37]. More interestingly, metal compounds (e.g., HAuCl4−) have been reported to reduce nanoparticles in situ via electroactive polymers, which provides a convenient way for metal particle catalysts [38]. However, in our previous reports, in situ reduction of metallic nanoparticles by electroactive polymers as catalysts for the reduction of 4-NP has not existed.
In our previous publication, AuNPs were successfully immobilized on polymers with amine functional groups on the electroactive polyamide [39]. Here, we prepared electroactive polyimide based on aniline pentamer (EPI-5) derivatives and configured them with different concentrations of Au ions to obtain Au nanoparticles on the surface of EPI-5 using in-situ redox reactions to form a series of catalysts to evaluate the efficiency and performance for the reduction of 4-NP.

2. Materials and Methods

2.1. Chemicals and Instrumentation

Aniline (99%, Alfa aesar, Lancashire, UK) distilled before use, ammonium peroxodisulfate (APS) (Thermo Fisher Scientific Inc., Waltham, MA, USA), Pyridine (98.9% Randor, J. T. Baker, PA, USA), N,N-dimethylformamide (DMF, J. T. Baker, PA, USA), N,N-dimethylacetamide (DMAc, Duksan, New Taipei, Taiwan), 4,4′-(4,4′-Isopropylidenediphenoxy)bis(phthalic anhydride) (BSAA, 97%, Sigma-Aldrich, St. Louis, MO, USA), 4,4′-diaminodiphenylamine sulfate hydrate (97%, TCI, Tokyo, Japan), N-Phenyl-p-phenylene diamine (98%, Alfa, Lancashire, UK), sodium chloride (NaCl, Sigma-Aldrich, St. Louis, MO, USA), hydrogen tetrachloroaurate(III)trihydrate (99%, HAuCl4.3H2O, Thermo Fisher Scientific Inc, Waltham, MA, USA), 4-nitrophenol (99%, Acros, Lancashire, UK), hydrochloric acid (37%, Fluka, NC, USA), acetic anhydride (99%, Fluka, NC, USA), ammonium hydroxide (25%, Fluka, NC, USA), sulfuric acid (97%, SHOWA, Tokyo, Japan), sodium borohydride (99%, Acros, Lancashire, UK), hydrazine (35%, Thermo Fisher Scientific Inc., Waltham, MA, USA).
1H-NMR (proton nucleus magnetic resonance spectroscopy, Agilent Technologies DD2, Santa Clara, CA, USA), FTIR spectra (Jasco FT/IR-4600, Tokyo, Japan) were used for the chemical structure of the electroactive material. GPC (gel permeation chromatography, Waters-150 CV, Milford, MA, USA) was used to determine the molecular weight of the sample. Cycle voltammetry (AutoLab, NLD, Utrecht, The Netherlands) was used for electroactive study. UV-Vis spectra (Jasco V-750, Tokyo, Japan) was measure the concentration of 4-Nitrophenol in the reaction during catalytic process and redox performance of the electroactive materials. The morphological were performed using high resolution transmission electron microscope (JEOL JEM-2010, Tokyo, Japan) and scanning electron microscopy (JEOL JSM-7100F, Tokyo, Japan). The formation of reduced AuNPs on the surface of EPI-5 was confirmed by X-ray diffraction analysis (PANalytical X’Pert3 powder diffractometer, Malvern Panalytical, Malvern, UK). The binding energy of the surface phase composition of the electroactive materials was recorded by x-ray photoelectron spectroscope (ULVAC-PHI, PHI 5000 VersaProbe, Chigasaki, Japan). Thermogravimetric analysis (TA Q500, USA) was used to calculate the AuNPs content in series Au/EPI-5.

2.2. Synthesis of Amino-Capped Aniline Trimer (ACAT)

Amino-capped Aniline Trimer (ACAT) was prepared by following the procedure reported by Yeh et al. [40]. First, aniline (1.5 g, 16.0 mmol) and 4, -4′-diaminondiphenylamibe sulfate (4.73 g, 16.0 mmol) were dissolved in HCl aqueous solution (1 M, 150 mL) containing 15 g of NaCl. A solution of ammonium persulfate (3.6 g, 16.0 mmol) in HCl aqueous solution (1 M, 25 mL) was added to the previously described solution maintained at 5 °C using a dropping funnel. The mixture was stirred for 1 h at 5 °C. The precipitate was collected through filtration, followed by washing with HCl aqueous solution (1 M, 150 mL). Then, the filtrate was washed with NH4OH solution (1 M, 300 mL) for 12 h and followed by washed with large amounts of distilled water. A black powder was further dried in dynamic vacuum oven at an operational temperature of 60 °C for 3 h to obtain ACAT, which was used in the next experiment to synthesize Amino-capped Aniline Pentamer.

2.3. Synthesis of Amino-Capped Aniline Pentamer (ACAP)

ACAT(1.5 g, 5.5 mmol) and N-phenyl-p-phenylene diamine(0.96 g, 5.5 mmol) were dissolved in the 50 mL of DMF at 5 °C. A solution of ammonium persulfate (0.91 g, 4.0 mmol) in HCl aqueous solution (1 M, 40 mL) were gradually doped into the above-mentioned solution at 5 °C while maintaining stirring for 3 h, followed by washing with mixture (12 mL DMF/12 mL 1 M HCl/12 mL DI water), precipitated, and collected by filtration, washed by NH4OH solution (1 M, 500 mL) for 12 h and followed by washed with large amounts of distilled water. A black powder was further dried in a vacuum oven at 60 °C for 5 h to obtain Amino-capped Aniline Pentamer (ACAP).

2.4. Synthesis of Electroactive Polyimide (EPI-5)

The electroactive polyimide (EPI-5) was synthesized using ACAP and BSAA. First, BSAA (0.52 g, 1.0 mmol) was added to 8.0 g of DMAc at room temperature with continuous stirring for 30 min. A solution containing ACAP (0.47 g, 1.0 mmol) in another 8.0 g of DMAc were prepared under magnetic stirring at room temperature. Dianhydride of BSAA was reacted with ACAP, followed by stirring for 24 h to generate electroactive poly (amic acid) (EPAA-5). The EPAA-5 was converted to electroactive polyimide by chemical imidization reaction. The reaction was done by adding the mixture of acetic anhydride/pyridine (0.102/0.079, v/v) to the previous solution containing EPAA-5 under stirring for 1 h and refluxing for 3 h under nitrogen. The as-prepared EPI-5 solution was slowly added dropwise to an excess amount of methanol to precipitate the product. After drying at 60 °C in the vacuum for 3 h to obtain electroactive polyimide based on ACAP (EPI-5).

2.5. Preparation of Series of Au/Electroactive Polyimide (Au/EPI-5) Composite

The series of Au/electroactive polyimide (Au/EPI-5) were prepared by the in-situ redox reaction between the EPI-5 and HAuCl4. First, 0.1 g as-prepared EPI-5 powder was dispersed into 10 mL of 1M NH4OH containing 3 mL of hydrazine solution. The mixture was stirred for 24 h, filtered, and washed with water until pH became neutralized, followed by freeze-drying treatment at −42 °C for 24 h. EPI-5(leucoemeraldine base) was collected in form of black powder. Series of Au/electroactive polyimide (Au/EPI-5) was prepared by immersing 0.1 g EPI-5(lucoemeraldine base) in 25 mL of different concentration (1, 3, 5 mM) HAuCl4•3H2O for 6 h. The Au/EPI-5 powder was subsequently collected by centrifugal filtration and followed by washing with excess amount of distilled water and freeze-drying treatment at −42 °C for 24 h, the as-prepared series Au/EPI-5 composites was collected as black powder. The synthetic route for EPI-5 decorated with Au nanoparticles is shown in Scheme 1.

2.6. Electrochemical Cyclic Voltammetry of EPI-5 and Series of Au/EPI-5 Composite

In this study, the redox property of as-prepared EPI-5 and series of Au/EPI-5 composites. EPI-5 and series of Au/EPI-5 composites were determined by coating the materials onto glass carbon electrode (working electrode), followed by a series of electrochemical cyclic voltammetry (CV) study. 0.01 g of EPI-5 and series of Au/EPI-5 composites were dissolved in 3 mL DMAc. These solutions were coating on the glass carbon electrode and dried at room temperature.

2.7. Catalytic Activity

To study the EPI-5 and series Au/EPI-5 composites were applied in the reduction reaction of 4-NP. NaBH4 was used as a hydrogen source in water. 0.5 mg EPI-5 and series Au/EPI-5 composites were dispersed in 3 mL of 4-NP. Then prepared 0.3 mL NaBH4 solution (100 mM) was introduced to the above 4-NP solution. And the time-dependent absorbance was recorded by UV-Vis absorption spectra. Finally, the kinetic rate constant, activation energy, and reusability of 4-NP were evaluated.

3. Results

3.1. Characterization of ACAT, ACAP, EPAA-5, and EPI-5

The representative 1H NMR spectra of ACAT and ACAP are shown in Figure 1 (includes subfigures of ACAT and ACAP chemical structures) to confirm the chemical structure. From Figure 1a, the spectra of ACAT reveals the signal at 5.42 ppm and 7.03 to 6.48 ppm corresponded to the primary amine protons (-NH2) and aromatic protons [40]. The signals of ACAP shows the signal at 5.41 ppm shown in Figure 1b could be also assigned to the primary amine protons(-NH2), and the signals around 7.03 to 6.60 ppm represents the splitting of aromatic protons [41].
In order to further confirm that ACAT and ACAP have been successfully synthesize, as-prepared ACAT and ACAP were characterized by FTIR, as shown in Figure 2. The results show the ACAT and ACAP have the same characteristic peak at 3309 and 3205 cm−1 corresponding to the -NH2 group. Moreover, the characteristic peak at position of 1598, 1498 cm−1, and 1596, 1500 cm−1 may be due to the vibration bands of quinoid rings and benzenoid rings of ACAT and ACAP, respectively. The characteristic peak of C-N on the amine group was detected at 1274 cm−1. Finally, the characteristic peaks were found at 834, 736, 697 cm−1 [41], which attributed to the bending of C-H group of the hydrogen atom at the benzene. These characteristic peaks of overall spectra indicated the ACAT and ACAP were successfully achieved.
As shown in Figure 2c,d, FTIR spectra used to characterize the structure of EPAA-5 and EPI-5 to further confirm the successful preparation. The FTIR spectra of EPAA-5 shows the main characteristic peak at 3200–3400 cm−1, corresponding hydroxy group (O-H) and amine group (N-H), and the carboxylic acid group (C=O) appeared at 1707 cm−1. In addition. The characteristic peak at 1598 and 1498 cm−1 were assigned to vibration bands of quinoid rings and benzenoid rings of EPAA-5, respectively. After reacting with anhydride/pyridine solution, the EPAA-5 was converted into EPI-5 by performing the chemical imidization. the characteristic peak of EPAA-5 at the position of 3200–3400 cm−1 was found to completely disappear, as shown in Figure 3. On the other hand, EPI-5 was found the asymmetric and symmetric carbonyl stretching vibration peak at 1776 and 1714 cm−1 [42]. EPI-5 was also observed at 1595 and 1500 cm−1, which represented the characteristic peak of quinoid rings and benzenoid rings. Based on the characteristic peaks of FTIR spectra, it indicated the complete conversion of EPAA-5 to EPI-5 by the chemical imidization reaction.

3.2. Chemical Oxidation of EPI-5

In this experiment, UV-Vis spectra can determine the redox properties of the EPI-5. The as-prepared leucoemeraldine base (fully reduction state) of the EPI-5 was dispersed in a DMAc solution. Subsequently, trace amounts of oxidant agent, (NH4)2S2O8, were gradually added to the EPI-5 solution reach the pernigraniline base (fully oxidation state), which was continuously monitored every 180 s of the sequential oxidation process of the EPI-5 in UV-Vis spectra, as shown in Figure 3. Firstly, two absorption peaks were appeared at position at 315 and 575 nm, which were associated with the π–π* transition of the conjugated ring system and the transition between the benzenoid ring and quinoid ring [43], respectively. After the addition of trace amounts of the oxidation agent, slow oxidation of ACAP segments in EPI-5 was observed. The absorption peaks found in UV-Vis spectra started a blue shift from 315 nm to 310 nm, which results accompanied by a decrease in intensity. At the same time, a new absorption peak appeared at 575 nm to 570 nm [44], which was related to the excitation-type transition between the HOMO orbital of the benzenoid ring and the LUMO orbital of the quinoid ring. Possible mechanism for this behavior can be interpreted as follows: Initially, EPI-5 reaches the LEB state of the ACAP segment through the reducing agent, hydrazine, and there is no quinone ring in the state. After adding a small amounts of oxidation agent, it reached first EB state with each ACAP segment containing only one quinone ring in this state. Finally, EPI-5 was oxidized to a PNB state with each ACAP segment containing two quinone ring in this state, it exhibited a blue shift, as shown in the inset in Figure 4. These results confirmed the chemical oxidation process of EPI-5.

3.3. Chemical Structural and Morphological Characterization of EPI-5 and Series Au/EPI-5

3.3.1. Characterization of EPI-5 and Series of Au/EPI-5 Composites by FT-IR

Figure 4 show the representative FT-IR of the EPI-5 and series Au/EPI-5 composites, respectively. FT-IR spectra of EPI-5 and series Au/EPI-5 showed the characteristic peaks around 1776 and 1714 cm−1 corresponding to asymmetric and symmetric carbonyl stretching vibration. The characteristic peaks around 1595 and 1500 cm−1 are attributed to the stretching vibration of C=C in the quinoid (Q) and benzenoid ring (B), respectively. These results indicate that the in-situ redox reaction between Au ions and EPI-5 is reduced on the surface of EPI-5 without changing the structure.
It should be noted that, with the increase of reduced AuNPs in the composites, the intensity of C=C stretching vibration for quinoid rings increases obviously. in addition, the intensity of C=C stretching vibration for benzenoid ring decrease was observed. Ascribed to the redox reaction between Au ions and EPI-5, leading to a decrease in the intensity ratio of benzene rings (B) to quinone rings (Q) with increasing amounts of reduced AuNPs [44]. Indicating the ratio of benzene rings(B) to quinone rings (Q) according to Table 1.
The TGA analysis curves of EPI-5 and series of Au/EPI-5 composites in an air atmosphere and shown in Figure 5. The main purpose is to completely creak the electroactive materials and determine the loading of Au on the EPI-5 surface. After the process, the residue contents of EPI-5 and series of Au/EPI-5 were 1.44%, 6.17%, 12.30% and 18.90%, respectively, which can be utilized to calculate the Au content in the Au/EPI-5 composite. Indicating the loading of Au according to Table 1.
The XRD patterns of the EPI-5 and series of Au/EPI-5 composites are shown in Figure 6. It can be seen that as compared to EPI-5 and series of Au/EPI-5 composites showed four additional characteristic peaks at 2θ of 38.1°, 44.3°, 64.5°, and 77.4°,which are ascribed to the (111), (200), (220), and (311) crystallographic planes of Au [45], respectively. This result shows that the AuNPs were reduced and anchored on the EPI-5 surface, the intensity of the characteristic peaks also increases as the amounts of reduced AuNPs increase.
The surface chemical composition of the EPI-5 and series of Au/EPI-5 composites was also investigated by XPS analysis. Figure 7 displays the full survey scan spectra and high solution XPS spectrum of various elements present in all materials. The survey scans spectra of EPI-5 and series of Au/EPI-5 reveal clear signals of Au 4f, C 1s, N 1s, and O 1s at 83, 283, 398 and 530 eV, respectively. The spectra in Figure 7b display two diffused peaks with binding energies of 82.2–85.5 and 85.9–86.1 eV, which correspond well with Au 4f7/2 and Au 4f5/2 spin-orbit splitting of metallic gold (Au0) [46], respectively. The appearance of Au0 is attributed to the redox reaction between oligoaniline segments and Au ions. Moreover, some reports that the interaction between mental nanoparticles and conductive polymer composite, Yang and coworkers [47] studies the Fe-PANI composite catalyst and explore the interaction between the Fe atom and N groups to reveal the catalytic site more clearly on Fe-PANI. Getting or losing electrons would certainly influence the chemical structure of electroactive polymers due to their redox properties. Therefore, with the electron transfer between AuNPs and EPI-5, the oxidation or the reducing state of EPI-5 would be changed. As shown in Figure 7c,d, the N 1s core-level spectra of EPI-5 and 5Au/EPI-5 were determined to further reveal the different chemical states of the N groups. The three different electronic states peak at 397.4–397.1, 398.9 and 402.0–401.4 eV were assigned to the benzenoid amine (-NH-), quinoid amine (=NH-), and nitrogen cationic radical (N+) groups [48,49], respectively. Quantification and identification of N species over EPI-5 and 5Au/EPI-5 for N 1s core-level spectra data were summarized in Table 2. The ratio of N+ species (sum of =NH- and N+) to N species (-NH-) was calculated to evaluate the electron transfer between AuNPs and EPI-5. The N+/N ratio was 0.56 and 2.74 for the EPI-5 and 5Au/EPI-5, respectively. It means that after reducing the AuNPs on the EPI-5 surface, EPI-5 loses a lot of electrons and was oxidized by in situ redox reaction between Au ions and EPI-5. Similar to the FTIR results, the content of =N- was increased after the loading of Au, which indicated that AuNPs coordinated with the -N= group are more energy favorable than that with the -NH- group. According to the XPS analysis results, the possible series of Au/EPI-5 composite formation process is consistent with the XRD and FTIR results.
The morphologies of the EPI-5 and series of Au/EPI-5 composites were characterized by SEM and HR-TEM, as shown in Figure 8. Compared with the morphology of the EPI-5, the AuNPs were clearly observed in the series of Au/EPI-5 composites, which showed that they were regularly dispersed. After loading the AuNPs, many black dots with average particle size in the range of 23–113 nm (as shown in the inset image of Figure 8f–h) can be observed on the EPI-5 surface, which indicates that AuNPs were anchored on the EPI-5, the particle size of the reduced AuNPs increases with the increase of the concentration.

3.3.2. Electroactive Properties of EPI-5 and Series of Au/EPI-5 Composites by Electrochemical CV Studies

In this study, all as-prepared EPI-5 and series of Au/EPI-5 composites were measured by cyclic voltammograms (CV) using the three-electrode electrochemical cell in 40 mL H2SO4 solution at a scan rate of 50 mV·s−1, as shown in Figure 9. The results show the bare GCE did not exhibit a redox peak. The CV curve of EPI-5 was observed with a relatively small peak of oxidation current at 0.78 μA. Moreover, the AuNPs were reduced and anchored on the EPI-5 surface showed in an increasing in redox current. The series of Au/EPI-5 showed an increase trend: 1Au/EPI-5 < 3Au/EPI-5 < 5Au/EPI-5, this current enhancement phenomenon indicates the AuNPs transforming higher electron transfer [50]. As we expected that the reduction of the higher concentration of AuNPs on the surface of EPI-5 do effectively enhance the redox capability, which is in line with FTIR, TGA, XRD, XPS, and HR-TEM analysis.

3.4. Catalytic Characterization of EPI-5 and Series of Au/EPI-5 Composites

To evaluate the catalytic activity of the prepared EPI-5 and series of Au/EPI-5 composites, the reduction of 4-NP to 4-AP has been chosen as a model reaction in the presence of excess NaBH4, which can be monitored by time-dependent UV-Vis spectroscopy. The absorption peak at 317 nm was attributed to the 4-NP solution. During the experiment, after addition of freshly prepared NaBH4 in the 4-NP solution, the phenolic hydroxyl group in 4-NP loses a proton, 4-NP ions are formed, and the absorption peak was shifted to 400 nm. 10 min after addition of the EPI-5 to the mixed solution of NaBH4 and 4-NP, the absorption peak was hardly change at 400 nm [51]. Notably, EPI-5 had the lower catalytic activity of catalytic reduction of 4-NP to 4-AP, which acted as catalyst carriers, as shown in Figure 10.
However, when adding a series of Au/EPI-5 composites (as shown in Figure 11), a new absorption peak was observed at 300 indicating the formation of 4-AP. At the same time, the absorption peak reduces of 4-NP with increasing peak strength of 4-AP. The completely reduction of 4-NP to 4-AP take about 17 min when 5Au/EPI-5 is used as the catalyst, it shows the best catalytic activity. And for 1Au/EPI-5 and 3Au/EPI-5, which are take about 43 min and 25 min. these results show the AuNPs is an essential substance for catalyst, and their characteristics affect the catalytic activity [52,53]. We can get the order of catalytic activity: 5Au/EPI-5 > 3Au/EPI-5 > 1Au/EPI-5, which may be attributed to the successful loading of Au (reference TGA analysis) and the electronic metal-support interactions between the EPI-5 and AuNPs. Specifically, the absorbed BH4− donates electrons to the AuNPs, and the electron transfer between EPI-5 and AuNPs would facilitate the electron donation of BH4−. Additionally, Au0 was confirmed in the EPI-5 by XPS analysis, and they could act as electron acceptor facilitating the electron transfer and the reduction of 4-NP, which endows the catalyst with excellent catalytic stability [54].
As the concentration of 4-NP was much lower than the NaBH4, the reduction of 4-NP to 4-AP can be regarded as the pseudo-first-order reaction kinetics. The rate constant was obtained using the following Equation (1) [55]:
l n C t C 0 = l n A t A 0 = − k · t
where Ct and C0 are the concentration of 4-NP at time t = 0 and t = t, respectively, which are corresponding to absorptance (At and A0) at 400 nm, and k is the rate constant. As shown in Figure 12a, the rate of the reaction were determined from the slopes of the linear relation plot of ln (Ct/C0) versus t using the series Au/EPI-5 composites. The values of k for 1Au/EPI-5, 3Au/EPI-5 and 5Au/EPI-5 are 7.0 × 10−4 s−1, 9.0 × 10−4 s−1, and 1.1 × 10−3 s−1, respectively. It was evident the 5Au/EPI-5 showed higher reactivity than the other Au/EPI-5 composites, the rate constant values were found to increase with increase loading of Au. In addition, based on the Arrhenius equation [56], the activation energy (Ea) for the reaction was determined using the following Equation (2):
ln k = ln A − E a R 1 T
where k is the rate constant at different temperature T(K), A is the Arrhenius factor, and Ea is the activation energy. As shown in Figure 12b, Ea can be obtained from the slope of lnk versus 1/T. The Ea of the 5Au/EPI-5 was determined from the Arrhenius plot to be 38.9 kJ/mol.
In addition to the careful catalytic studies, reusability of heterogeneous catalysts is important properties and vital factor of treating pollutants. In a recycle experiment, the 5Au/EPI-5 composite was carefully collected and used for multiple catalytic reactions after waiting for the catalyst to settle slowly for one day after the reduction reaction. As shown in Figure 13, after ten cycles, the conversion of 4-NP still above 95% which indicates the 5Au/EPI-5 developed in the current study shows excellent catalytic stability and robust even a after multiple uses.
The rate constant and the recyclable of the 5Au/EPI-5 composite comparable to those of most catalyst using conjugate polymer as a carrier in the literature and previously published reports (Table 3). The catalytic activity and reusability observed in this work were better than those observed in several reports.

3.5. Possible Reduction Reaction Mechanism for 4-NP

To explain the process of the catalytic reduction of 4-NP to 4-AP using the series Au/EPI-5 composites, a possible mechanism for the reduction of 4-NP was proposed based on the Langmuir-Hinshelwood mechanism (as shown in Scheme 2). The ionization of NaBH4 in the liquid results in the production of BH4− and their adsorption AuNPs on the EPI-5 to form hydride complex (Au-H species). At the same time, 4-NP ions adsorb on the hydride complex surface. Then Au-H species are transferred to the adsorbed 4-NP and lead to the reduction of -NO2. After three step catalytic hydro-dehydration reaction to generate the corresponding 4-AP. Finally, 4-AP desorbs form the catalyst [60,61].

4. Conclusions

In this work, an electroactive polyimide decorated with AuNPs (Au/EPI-5) without the addition of any reducing agent was successfully synthesized and reduced 4-NP to 4-AP. The AuNPs were loaded on the Au/EPI-5 by the in-situ redox reaction between the EPI-5 and HAuCl4. Through the comparison of catalytic performance of series Au/EPI-5, we find the 5Au/EPI-5 exhibited the best catalytic activity, which could be attributed to the high loading of AuNPs and the synergistic effect between the EPI-5 and AuNPs. Results showed the rate constant, activation energy of the 5Au/EPI-5 catalyzed reduction of 4-NP were 1.1 × 10−3 s−1 and 38.9 kJ/mol, respectively, and after 10 cycles, the 5Au/EPI-5 composite maintained at 95% above. In summary, this Au/EPI-5 composite demonstrates many advantages, such as reduction using very low catalyst amount (0.5 mg), remarkable catalytic performance, and excellent recyclability. Making electroactive polymers as a carrier for AuNPs attractive for the catalytic field.

Author Contributions

Y.-S.C. was involved in data curation, investigation, writing—original draft, methodology, validation, software. W.-Z.S. assisted with data preparation & validation. K.-H.L. was provided of study materials, reagents, and data validation. J.-M.Y. and M.-H.T. provided supervision for the research and provided the methodology. All authors have read and agreed to the published version of the manuscript.

Funding

This research received external funding form the Ministry of Science and Technology of Taiwan (grant No. MOST -111-2221-E-167 -001-).

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Acknowledgments

We would like to thank the Ministry of Science and Technology of Taiwan under the grant number of MOST -111-2221-E-167 -001-for the financial support.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Xu, Y.; Shi, X.; Hua, R.; Zhang, R.; Yao, Y.; Zhao, B.; Liu, T.; Zheng, J.; Lu, G. Remarkably catalytic activity in reduction of 4-nitrophenol and methylene blue by Fe3O4@ COF supported noble metal nanoparticles. Appl. Catal. B Environ. 2020, 260, 118142. [Google Scholar] [CrossRef]
  2. Abdelhamid, H.N. High performance and ultrafast reduction of 4-nitrophenol using metal-organic frameworks. J. Environ. Chem. Eng. 2021, 9, 104404. [Google Scholar] [CrossRef]
  3. Hauchman, F.S. US Environmental Protection Agency Health-Effects Research on Drinking-Water Contaminants; Environmental Protection Agency: Research Triangle Park, NC, USA, 1992.
  4. Liu, S.; Wang, J.; Huang, W.; Tan, X.; Dong, H.; Goodman, B.A.; Du, H.; Lei, F.; Diao, K. Adsorption of phenolic compounds from water by a novel ethylenediamine rosin-based resin: Interaction models and adsorption mechanisms. Chemosphere 2019, 214, 821–829. [Google Scholar] [CrossRef]
  5. Zhang, Y.; Xiao, Y.; Liu, X.; Yin, Z.; Cao, S. Silver/carbon co-decorated hollow TiO2 catalyst drives the efficient photocatalytic degradation/catalytic hydrogenation of 4-nitrophenol. J. Taiwan Inst. Chem. Eng. 2022, 133, 104274. [Google Scholar] [CrossRef]
  6. Sarkar, P.; Dey, A. 4-Nitrophenol biodegradation by an isolated and characterized microbial consortium and statistical optimization of physicochemical parameters by Taguchi Methodology. J. Environ. Chem. Eng. 2020, 8, 104347. [Google Scholar] [CrossRef]
  7. Menazea, A.; Mostafa, A.M. Ag doped CuO thin film prepared via pulsed laser deposition for 4-nitrophenol degradation. J. Environ. Chem. Eng. 2020, 8, 104104. [Google Scholar] [CrossRef]
  8. Chu, Y.; Miao, B.; Zhang, X.; Lv, R. Heterogeneous electro-Fenton-like oxidation for the degradation of 4-nitrophenol characterized by immobilized Fe (III): Performance, mechanism and chlorinated organic compounds formation. J. Water Process Eng. 2020, 38, 101662. [Google Scholar] [CrossRef]
  9. Hu, L.; Liu, X.; Guo, A.; Wu, J.; Wang, Y.; Long, Y.; Fan, G. Cobalt with porous carbon architecture: Towards of 4-nitrophenol degradation and reduction. Sep. Purif. Technol. 2022, 288, 120595. [Google Scholar] [CrossRef]
  10. Liang, W.; Lu, Y.; Li, N.; Li, H.; Zhu, F. Microwave-assisted synthesis of magnetic surface molecular imprinted polymer for adsorption and solid phase extraction of 4-nitrophenol in wastewater. Microchem. J. 2020, 159, 105316. [Google Scholar] [CrossRef]
  11. Mejía, Y.R.; Bogireddy, N.K.R. Reduction of 4-nitrophenol using green-fabricated metal nanoparticles. RSC Adv. 2022, 12, 18661–18675. [Google Scholar] [CrossRef] [PubMed]
  12. Corbett, J.F. An historical review of the use of dye precursors in the formulation of commercial oxidation hair dyes. Dye Pigment. 1999, 41, 127–136. [Google Scholar] [CrossRef]
  13. Lunar, L.; Sicilia, D.; Rubio, S.; Pérez-Bendito, D.; Nickel, U. Degradation of photographic developers by Fenton’s reagent: Condition optimization and kinetics for metol oxidation. Water Res. 2000, 34, 1791–1802. [Google Scholar] [CrossRef]
  14. Chang, Y.-C.; Chen, D.-H. Catalytic reduction of 4-nitrophenol by magnetically recoverable Au nanocatalyst. J. Hazard. Mater. 2009, 165, 664–669. [Google Scholar] [CrossRef]
  15. Hao, B.; Lu, G.; Zhang, S.; Li, Y.; Ding, A.; Huang, X. Gold nanoparticles standing on PEG/PAMAM/thiol-functionalized nanographene oxide as aqueous catalysts. Polym. Chem. 2020, 11, 4094–4104. [Google Scholar] [CrossRef]
  16. Al-Kahtani, A.A.; Almuqati, T.; Alhokbany, N.; Ahamad, T.; Naushad, M.; Alshehri, S.M. A clean approach for the reduction of hazardous 4-nitrophenol using gold nanoparticles decorated multiwalled carbon nanotubes. J. Clean. Prod. 2018, 191, 429–435. [Google Scholar] [CrossRef]
  17. Azharuddin, M.; Zhu, G.H.; Das, D.; Ozgur, E.; Uzun, L.; Turner, A.P.; Patra, H.K. A repertoire of biomedical applications of noble metal nanoparticles. Chem. Commun. 2019, 55, 6964–6996. [Google Scholar] [CrossRef]
  18. John, A.; Benny, L.; Cherian, A.R.; Narahari, S.Y.; Varghese, A.; Hegde, G. Electrochemical sensors using conducting polymer/noble metal nanoparticle nanocomposites for the detection of various analytes: A review. J. Nanostruct. Chem. 2021, 11, 1–31. [Google Scholar] [CrossRef]
  19. Futamura, S.; Muramoto, A.; Tachikawa, Y.; Matsuda, J.; Lyth, S.M.; Shiratori, Y.; Taniguchi, S.; Sasaki, K. SOFC anodes impregnated with noble metal catalyst nanoparticles for high fuel utilization. Int. J. Hydrogen Energy 2019, 44, 8502–8518. [Google Scholar] [CrossRef]
  20. Liu, D.; Barbar, A.; Najam, T.; Javed, M.S.; Shen, J.; Tsiakaras, P.; Cai, X. Single noble metal atoms doped 2D materials for catalysis. Appl. Catal. B Environ. 2021, 297, 120389. [Google Scholar] [CrossRef]
  21. Das, R.; Sypu, V.S.; Paumo, H.K.; Bhaumik, M.; Maharaj, V.; Maity, A. Silver decorated magnetic nanocomposite (Fe3O4@ PPy-MAA/Ag) as highly active catalyst towards reduction of 4-nitrophenol and toxic organic dyes. Appl. Catal. B Environ. 2019, 244, 546–558. [Google Scholar] [CrossRef]
  22. Lai, G.-H.; Huang, T.-C.; Pai, Y.-H.; Huang, B.-S.; Tsai, M.-H.; Yang, T.-I.; Chung, Y.-H. Preparation of highly-stable and recyclable novel Au/ZrP composite catalyst for 4-nitrophenol reduction. J. Taiwan Inst. Chem. Eng. 2019, 95, 525–531. [Google Scholar] [CrossRef]
  23. Das, T.K.; Ghosh, S.K.; Das, N.C. Green synthesis of a reduced graphene oxide/silver nanoparticles-based catalyst for degradation of a wide range of organic pollutants. Nano-Struct. Nano-Objects 2023, 34, 100960. [Google Scholar] [CrossRef]
  24. Wu, Z.; Zhu, J.; Wen, W.; Zhang, X.; Wang, S. Spherical covalent organic framework supported Cu/Ag bimetallic nanoparticles with highly catalytic activity for reduction of 4-nitrophenol. J. Solid State Chem. 2022, 311, 123116. [Google Scholar] [CrossRef]
  25. Khan, A.; Wei, D.; Wang, Z.; Su, X.; Wang, J.; Alam, S.; Wang, L.; Wu, R.; Maloletnev, A.S.; Yang, C. MOF-derived nickel–cobalt bimetal oxide nanostructures as a cooperative catalyst for the reduction of 4-nitrophenol. J. Chem. Technol. Biotechnol. 2021, 96, 697–703. [Google Scholar] [CrossRef]
  26. Wang, M.; Tang, X.-H.; Cai, J.-H.; Wu, H.; Shen, J.-B.; Guo, S.-Y. Construction, mechanism and prospective of conductive polymer composites with multiple interfaces for electromagnetic interference shielding: A review. Carbon 2021, 177, 377–402. [Google Scholar] [CrossRef]
  27. Sun, L.; Yin, Z.; Zhang, J.; Ren, X.; Zhang, M.; Song, W.; Xu, Z.; Qi, C. Gold nanoparticles supported on poly (aniline-co-pyrrole) as the efficient catalysts for the reduction of 4-nitrophenol. Mol. Catal. 2022, 525, 112362. [Google Scholar] [CrossRef]
  28. Yan, J.; Yang, L.; Cui, M.; Wang, X.; Chee, K.J.; Nguyen, V.C.; Kumar, V.; Sumboja, A.; Wang, M.; Lee, P.S. Aniline Tetramer-Graphene Oxide Composites for High Performance Supercapacitors. Adv. Energy Mater. 2014, 4, 1400781. [Google Scholar] [CrossRef]
  29. Chen, L.; Yu, Y.; Mao, H.; Lu, X.; Zhang, W.; Wei, Y. Synthesis of parent aniline tetramer and pentamer and redox properties. Mater. Lett. 2005, 59, 2446–2450. [Google Scholar] [CrossRef]
  30. Cai, Y.; Wang, H.; Qi, F.; Dong, Z.; Mu, J.; Qiu, X. Synthesis and electrochemical properties of polyimide containing nona-aniline. React. Funct. Polym. 2022, 178, 105333. [Google Scholar] [CrossRef]
  31. Wang, Y.; Jia, X.; Berda, E.B.; Zhao, J.; Liu, X.; Chao, D. Design and synthesis of multicolor electrochromic polymers based on oligoaniline and viologen/phenothiazine groups. Eur. Polym. J. 2020, 138, 109979. [Google Scholar] [CrossRef]
  32. Zhang, Y.; Tang, J.; Fang, W.; Zhao, Q.; Lei, X.; Zhang, J.; Chen, J.; Li, Y.; Zuo, Y. Synergetic Effect of Electrical and Topographical Cues in Aniline Trimer-Based Polyurethane Fibrous Scaffolds on Tissue Regeneration. J. Funct. Biomater. 2023, 14, 185. [Google Scholar] [CrossRef]
  33. Huang, T.-C.; Yeh, L.-C.; Lai, G.-H.; Huang, B.-S.; Yang, T.-I.; Hsu, S.-C.; Lo, A.-Y.; Yeh, J.-M. Advanced superhydrophobic electroactive fluorinated polyimide and its application in anticorrosion coating. Int. J. Green Energy 2017, 14, 113–120. [Google Scholar] [CrossRef]
  34. Ji, W.-F.; Chu, C.-M.; Hsu, S.-C.; Lu, Y.-D.; Yu, Y.-C.; Santiago, K.S.; Yeh, J.-M. Synthesis and characterization of organo-soluble aniline oligomer-based electroactive doped with gold nanoparticles, and application to electrochemical sensing of ascorbic acid. Polymer 2017, 128, 218–228. [Google Scholar] [CrossRef]
  35. Chang, C.W.; Yen, H.J.; Huang, K.Y.; Yeh, J.M.; Liou, G.S. Novel organosoluble aromatic polyimides bearing pendant methoxy-substituted triphenylamine moieties: Synthesis, electrochromic, and gas separation properties. J. Polym. Sci. Part A Polym. Chem. 2008, 46, 7937–7949. [Google Scholar] [CrossRef]
  36. Huang, T.-C.; Yeh, T.-C.; Huang, H.-Y.; Ji, W.-F.; Chou, Y.-C.; Hung, W.-I.; Yeh, J.-M.; Tsai, M.-H. Electrochemical studies on aniline-pentamer-based electroactive polyimide coating: Corrosion protection and electrochromic properties. Electrochim. Acta 2011, 56, 10151–10158. [Google Scholar] [CrossRef]
  37. Chen, H.; Zhuang, Q.; Wang, H.; Zhai, X.; Zhang, K.; Deng, H.; Dong, W.; Xie, A. Ultrafine gold nanoparticles dispersed in conjugated microporous polymers with sulfhydryl functional groups to improve the reducing activity of 4-nitrophenol. Colloids Surf. A Physicochem. Eng. Asp. 2022, 649, 129459. [Google Scholar] [CrossRef]
  38. Sun, L.; Jiang, L.; Peng, S.; Zheng, Y.; Sun, X.; Su, H.; Qi, C. Preparation of Au catalysts supported on core-shell SiO2/polypyrrole composites with high catalytic performances in the reduction of 4-nitrophenol. Synth. Met. 2019, 248, 20–26. [Google Scholar] [CrossRef]
  39. Lai, G.-H.; Huang, B.-S.; Yang, T.-I.; Tsai, M.-H.; Chou, Y.-C. Preparation of highly stable and recyclable Au/electroactive polyamide composite catalyst for nitrophenol reduction. Polymer 2021, 213, 123200. [Google Scholar] [CrossRef]
  40. Padua, L.M.G.; Yeh, J.-M.; Santiago, K.S. A novel application of electroactive polyimide doped with gold nanoparticles: As a chemiresistor sensor for hydrogen sulfide gas. Polymers 2019, 11, 1918. [Google Scholar] [CrossRef] [Green Version]
  41. Lan, Y.-X.; Weng, C.W.; Ahmed, M.M.; Luo, K.-H.; Ji, W.-F.; Liu, W.-R.; Yeh, J.-M. Aniline pentamer-modified reduced graphene oxide/epoxy composites as anticorrosion coatings. Mater. Chem. Phys. 2021, 264, 124446. [Google Scholar] [CrossRef]
  42. Tsai, M.; Lu, S.; Lai, Y.; Lai, G.; Dizon, G.; Yang, T.; Lin, Y.; Chou, Y. Novel ascorbic acid sensor prepared from gold/aniline-pentamer-based electroactive polyamide composites. Express Polym. Lett. 2018, 12, 71–81. [Google Scholar] [CrossRef]
  43. Yeh, L.-C.; Huang, T.-C.; Huang, Y.-P.; Huang, H.-Y.; Chen, H.-H.; Yang, T.-I.; Yeh, J.-M. Synthesis electroactive polyurea with aniline-pentamer-based in the main chain and its application in electrochemical sensor. Electrochim. Acta 2013, 94, 300–306. [Google Scholar] [CrossRef]
  44. Yan, Y.; Li, F.; Hanlon, A.M.; Berda, E.B.; Liu, X.; Wang, C.; Chao, D. Electrochemical performance of electroactive poly (amic acid)-Cu2+ composites. Appl. Surf. Sci. 2017, 392, 1–7. [Google Scholar] [CrossRef] [Green Version]
  45. Liu, F.; Liu, X.; Liu, W.; Gu, H. ROMP synthesis of gallol-containing polymer hydrogels for in situ fabrication of AuNPs and AgNPs composites as recyclable catalysts for the degradation of 4-nitrophenol. Polymer 2021, 219, 123539. [Google Scholar] [CrossRef]
  46. Sun, L.; Jiang, L.; Zhang, J.; Murayama, T.; Zhang, M.; Zheng, Y.; Su, H.; Qi, C. Preparation of polyaniline microtubes as the gold catalyst support with improved catalytic performances for the reduction of nitrophenols. Top. Catal. 2021, 64, 215–223. [Google Scholar] [CrossRef]
  47. Shi, B.; Li, H.; Fu, X.; Zhao, C.; Li, M.; Liu, M.; Yan, W.; Yang, H. Fe Single-Atom Catalyst for Cost-Effective yet Highly Efficient Heterogeneous Fenton Catalysis. ACS Appl. Mater. Interfaces 2022, 14, 53767–53776. [Google Scholar] [CrossRef] [PubMed]
  48. Han, H.; Lee, S.W.; Moon, K.H.; Cho, S. Fabrication of solid-state asymmetric supercapacitors based on aniline oligomers and graphene electrodes with enhanced electrochemical performances. ACS Omega 2019, 4, 1244–1253. [Google Scholar] [CrossRef] [PubMed]
  49. Weng, C.-J.; Hsu, P.-H.; Hsu, S.-C.; Chang, C.-H.; Hung, W.-I.; Wu, P.-S.; Yeh, J.-M. Synthesis of electroactive mesoporous gold–organosilica nanocomposite materials via a sol–gel process with non-surfactant templates and the electroanalysis of ascorbic acid. J. Mater. Chem. B 2013, 1, 4983–4991. [Google Scholar] [CrossRef]
  50. Latif, H.; Wasif, D.; Rasheed, S.; Sattar, A.; Rafique, M.S.; Anwar, A.W.; Zaheer, S.; Shabbir, S.A.; Imtiaz, A.; Qutab, M. Gold nanoparticles mixed multiwall carbon nanotubes, supported on graphene nano-ribbons (Au-NT-G) as an efficient reduction electrode for Polymer Electrolyte Membrane fuel cells (PEMFC). Renew. Energy 2020, 154, 767–773. [Google Scholar] [CrossRef]
  51. Balamurugan, A.; Ho, K.-C.; Chen, S.-M. One-pot synthesis of highly stable silver nanoparticles-conducting polymer nanocomposite and its catalytic application. Synth. Met. 2009, 159, 2544–2549. [Google Scholar] [CrossRef]
  52. Lai, G.-H.; Chou, Y.-C.; Huang, B.-S.; Yang, T.-I.; Tsai, M.-H. Application of electroactive Au/aniline tetramer–graphene oxide composites as a highly efficient reusable catalyst. RSC Adv. 2021, 11, 71–77. [Google Scholar] [CrossRef]
  53. Song, S.G.; Satheeshkumar, C.; Park, J.; Ahn, J.; Premkumar, T.; Lee, Y.; Song, C. N-heterocyclic carbene-based conducting polymer–gold nanoparticle hybrids and their catalytic application. Macromolecules 2014, 47, 6566–6571. [Google Scholar] [CrossRef]
  54. Lai, G.-H.; Huang, T.-C.; Huang, B.-S.; Chou, Y.-C. A novel Au/electroactive poly (amic acid) composite as an effective catalyst for p-nitrophenol reduction. RSC Adv. 2021, 11, 33990–33995. [Google Scholar] [CrossRef]
  55. Kumar, A.; Belwal, M.; Maurya, R.R.; Mohan, V.; Vishwanathan, V. Heterogeneous catalytic reduction of anthropogenic pollutant, 4-nitrophenol by Au/AC nanocatalysts. Mater. Sci. Energy Technol. 2019, 2, 526–531. [Google Scholar] [CrossRef]
  56. Kohantorabi, M.; Gholami, M.R. Fabrication of novel ternary Au/CeO2@gC3N4 nanocomposite: Kinetics and mechanism investigation of 4-nitrophenol reduction, and benzyl alcohol oxidation. Appl. Phys. A 2018, 124, 1–17. [Google Scholar] [CrossRef]
  57. Wang, H.; Liao, Q.; Xi, K. Synthesis of melamine-based crystalline porous polymers and its silver-doped composites with one-pot approach for catalytic reduction of 4-nitrophenol. Microporous Mesoporous Mater. 2022, 346, 112297. [Google Scholar] [CrossRef]
  58. Ma, J.; Deng, H.; Zhang, Z.; Zhang, L.; Qin, Z.; Zhang, Y.; Gao, L.; Jiao, T. Facile synthesis of Ag3PO4/PPy/PANI ternary composites for efficient catalytic reduction of 4-nitrophenol and 2-nitroaniline. Colloids Surf. A Physicochem. Eng. Asp. 2022, 632, 127774. [Google Scholar] [CrossRef]
  59. Guo, M.; Zhang, Y.; Du, F.; Wu, Y.; Zhang, Q.; Jiang, C. Silver nanoparticles/polydopamine coated polyvinyl alcohol sponge as an effective and recyclable catalyst for reduction of 4-nitrophenol. Mater. Chem. Phys. 2019, 225, 42–49. [Google Scholar] [CrossRef]
  60. Sypu, V.S.; Bhaumik, M.; Raju, K.; Maity, A. Nickel hydroxide nanoparticles decorated napthalene sulfonic acid-doped polyaniline nanotubes as efficient catalysts for nitroarene reduction. J. Colloid Interface Sci. 2021, 581, 979–989. [Google Scholar] [CrossRef]
  61. Dey, C.; De, D.; Nandi, M.; Goswami, M.M. A high performance recyclable magnetic CuFe2O4 nanocatalyst for facile reduction of 4-nitrophenol. Mater. Chem. Phys. 2020, 242, 122237. [Google Scholar] [CrossRef]
Polymers 15 02664 sch001 550
Scheme 1. Possible mechanism for the formation of series Au/EPI-5 composites with different HAuCl4 concentrations.
Scheme 1. Possible mechanism for the formation of series Au/EPI-5 composites with different HAuCl4 concentrations.
Polymers 15 02664 sch001
Polymers 15 02664 g001 550
Figure 1. Characterization of ACAT and ACAP as determined by 1H NMR.
Figure 1. Characterization of ACAT and ACAP as determined by 1H NMR.
Polymers 15 02664 g001
Polymers 15 02664 g002 550
Figure 2. FT-IR spectra of (a–d).
Figure 2. FT-IR spectra of (a–d).
Polymers 15 02664 g002
Polymers 15 02664 g003 550
Figure 3. Chemical oxidation of EPI-5 by UV-Vis spectra.
Figure 3. Chemical oxidation of EPI-5 by UV-Vis spectra.
Polymers 15 02664 g003
Polymers 15 02664 g004a 550Polymers 15 02664 g004b 550
Figure 4. FT-IR spectra in the range 1000–1800 cm−1 of (a–d).
Figure 4. FT-IR spectra in the range 1000–1800 cm−1 of (a–d).
Polymers 15 02664 g004aPolymers 15 02664 g004b
Polymers 15 02664 g005 550
Figure 5. TGA diagram of the EPI-5 and series of Au/EPI-5 composites.
Figure 5. TGA diagram of the EPI-5 and series of Au/EPI-5 composites.
Polymers 15 02664 g005
Polymers 15 02664 g006 550
Figure 6. XRD pattern of (a) EPI-5, (b) 1Au/EPI-5, (c) 3Au/EPI-5, and (d) 5Au/EPI-5.
Figure 6. XRD pattern of (a) EPI-5, (b) 1Au/EPI-5, (c) 3Au/EPI-5, and (d) 5Au/EPI-5.
Polymers 15 02664 g006
Polymers 15 02664 g007a 550Polymers 15 02664 g007b 550
Figure 7. (a) XPS spectrum of EPI-5 and series of Au/EPI-5 composite, (b) Au 4f core- level XPS spectrum of series of Au/EPI-5 composite, N 1s core-level XPS spectrum of (c,d).
Figure 7. (a) XPS spectrum of EPI-5 and series of Au/EPI-5 composite, (b) Au 4f core- level XPS spectrum of series of Au/EPI-5 composite, N 1s core-level XPS spectrum of (c,d).
Polymers 15 02664 g007aPolymers 15 02664 g007b
Polymers 15 02664 g008 550
Figure 8. SEM images of (a) EPI-5, (b) 1Au/EPI-5, (c) 3Au/EPI-5, and (d) 5Au/EPI-5. HR-TEM images of (e) EPI-5, (f) 1Au/EPI-5 (g) 3Au/EPI-5 and (h) 5Au/EPI-5 (include particle size analysis).
Figure 8. SEM images of (a) EPI-5, (b) 1Au/EPI-5, (c) 3Au/EPI-5, and (d) 5Au/EPI-5. HR-TEM images of (e) EPI-5, (f) 1Au/EPI-5 (g) 3Au/EPI-5 and (h) 5Au/EPI-5 (include particle size analysis).
Polymers 15 02664 g008
Polymers 15 02664 g009 550
Figure 9. Electrochemical cyclic voltammetry for (a) GCE, (b) EPI-5, (c) 1Au/EPI-5, (d) 3Au/EPI-5, and (e) 5Au/EPI-5 as measured in 1.0 M H2SO4 aqueous solution with scan rate of 50 mV/s.
Figure 9. Electrochemical cyclic voltammetry for (a) GCE, (b) EPI-5, (c) 1Au/EPI-5, (d) 3Au/EPI-5, and (e) 5Au/EPI-5 as measured in 1.0 M H2SO4 aqueous solution with scan rate of 50 mV/s.
Polymers 15 02664 g009
Polymers 15 02664 g010 550
Figure 10. UV-Vis spectra of (a) 4-NP before (black) and after (red) the addition of NaBH4. Time-dependent reduction process of 4-NP after the addition of the (b) EPI-5.
Figure 10. UV-Vis spectra of (a) 4-NP before (black) and after (red) the addition of NaBH4. Time-dependent reduction process of 4-NP after the addition of the (b) EPI-5.
Polymers 15 02664 g010
Polymers 15 02664 g011a 550Polymers 15 02664 g011b 550
Figure 11. UV-Vis spectra of catalytic reduction 4-NP with NaBH4 in the presence of (a–c).
Figure 11. UV-Vis spectra of catalytic reduction 4-NP with NaBH4 in the presence of (a–c).
Polymers 15 02664 g011aPolymers 15 02664 g011b
Polymers 15 02664 g012 550
Figure 12. (a) The ln (Ct/C0) versus time for the catalytic reduction of 4-NP over series Au/EPI-5 composite catalyst. (b) Plot of lnk versus 1/T for 4-NP reduction catalyzed by the 5Au/EPI-5 composite in the presence of NaBH4 at different temperatures.
Figure 12. (a) The ln (Ct/C0) versus time for the catalytic reduction of 4-NP over series Au/EPI-5 composite catalyst. (b) Plot of lnk versus 1/T for 4-NP reduction catalyzed by the 5Au/EPI-5 composite in the presence of NaBH4 at different temperatures.
Polymers 15 02664 g012
Polymers 15 02664 g013 550
Figure 13. The reusability of 5Au/EPI-5 composites for catalytic reduction of 4-NP.
Figure 13. The reusability of 5Au/EPI-5 composites for catalytic reduction of 4-NP.
Polymers 15 02664 g013
Polymers 15 02664 sch002 550
Scheme 2. Catalytic mechanism of Au/EPI-5 in the reduction of 4-NP to 4-AP.
Scheme 2. Catalytic mechanism of Au/EPI-5 in the reduction of 4-NP to 4-AP.
Polymers 15 02664 sch002
Table
Table 1. Loading of Au and absorption strength of benzenoid ring and quinoid ring of EPI-5 and series of Au/EPI-5 composites.
Table 1. Loading of Au and absorption strength of benzenoid ring and quinoid ring of EPI-5 and series of Au/EPI-5 composites.
Benzene Ring
(1500 cm−1)		Quinone Ring
(1595 cm−1)		B/QLoading of Au
(wt.%) a
EPI-50.18290.08062.270
1Au/EPI-50.14230.08181.744.73
3Au/EPI-50.19080.11121.7110.86
5Au/EPI-50.15260.09321.6317.46
a Determined by the TGA analysis.
Table
Table 2. Quantification and identification of N species over EPI-5 and 5Au/EPI-5 for N 1s XPS data.
Table 2. Quantification and identification of N species over EPI-5 and 5Au/EPI-5 for N 1s XPS data.
CatalystsBinding Energies (eV)N Species (%)
-NH--N=N+-NH--N=N+
EPI-5397.4398.9402.063.928.27.9
5Au/EPI-5397.1398.9401.426.765.28.1
Table
Table 3. Catalytic efficiency of different catalysts for 4-NP catalytic reduction to 4-AP.
Table 3. Catalytic efficiency of different catalysts for 4-NP catalytic reduction to 4-AP.
CatalystWeight
(mg)		Rate Constant
(s−1)		Rate Constant
(min−1)		Recyclability
(Cycles)		Ref.
AuNPs-gel-G20-0.0815[46]
ME-BTCA-Ag-253.3 × 10−4--[57]
Ag3PO4/PPy/PANI1-0.005-[58]
AgNPs/D-PVA60-0.0724[59]
Fe3O4@PPy-MAA-Ag2.5-0.0058[21]
Au/ZrP11.8 × 10−2-10[22]
Au/EPA0.51.6 × 10−2-30[39]
5Au/EPI-50.51.1 × 10−30.06410This work
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Chen, Y.-S.; Shi, W.-Z.; Luo, K.-H.; Yeh, J.-M.; Tsai, M.-H. In Situ Redox Synthesis of Highly Stable Au/Electroactive Polyimide Composite and Its Application on 4-Nitrophenol Reduction. Polymers 2023, 15, 2664. https://doi.org/10.3390/polym15122664

AMA Style

Chen Y-S, Shi W-Z, Luo K-H, Yeh J-M, Tsai M-H. In Situ Redox Synthesis of Highly Stable Au/Electroactive Polyimide Composite and Its Application on 4-Nitrophenol Reduction. Polymers. 2023; 15(12):2664. https://doi.org/10.3390/polym15122664

Chicago/Turabian Style

Chen, Yi-Sheng, Wei-Zhong Shi, Kun-Hao Luo, Jui-Ming Yeh, and Mei-Hui Tsai. 2023. "In Situ Redox Synthesis of Highly Stable Au/Electroactive Polyimide Composite and Its Application on 4-Nitrophenol Reduction" Polymers 15, no. 12: 2664. https://doi.org/10.3390/polym15122664

APA Style

Chen, Y. -S., Shi, W. -Z., Luo, K. -H., Yeh, J. -M., & Tsai, M. -H. (2023). In Situ Redox Synthesis of Highly Stable Au/Electroactive Polyimide Composite and Its Application on 4-Nitrophenol Reduction. Polymers, 15(12), 2664. https://doi.org/10.3390/polym15122664

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop