Open Access Article
Pampa
Jhariat
b and
Tamas
Panda
*a
aCentre for Clean Environment, Vellore Institute of Technology, Vellore, Tamil Nadu 632014, India. E-mail: tamaskumarpanda@vit.ac.in
bDepartment of Chemistry, School of Advanced Sciences, Vellore Institute of Technology, Vellore, Tamil Nadu 632014, India
First published on 16th April 2024
A rise in the concentration of hazardous and noxious substances in the environment due to industrialization and population expansion has begun to disrupt the ecological equilibrium. It is of utmost importance to monitor and efficiently manage these pollutants through adsorption techniques or catalytic degradation. Viologen-based porous organic polymers (vPOPs) are a class of porous polymeric materials composed of 4.4′-bipyridinium ions along with other small organic molecules linked together by strong covalent bonds. They have garnered attention as a viable platform for many applications, particularly in the realm of effective environmental remediation. This advancement has generated prospects for the development of more advanced techniques for eliminating contaminants, segregating chemicals, converting gases, and transforming energy. The purpose of this study is to provide an overview of the most recent advancements and successes in the production, utilization, and structural engineering of vPOPs and associated composite materials to remediate environmental problems. This detailed study seeks to provide insights into the potential of vPOPs as viable materials for addressing environmental challenges and stimulating additional research in this emerging sector. This paper provides an analysis of the perspectives about the challenges, opportunities, practical applications, and prospects of these materials in advanced remediation technology for the next generation.
The rise and notable advancement of porous materials in recent years have highlighted the significant influence of porosity in enhancing the outstanding performance of a material across many applications.9,10 Porous materials are crucial for many developing technologies and applications because of their unique inherent qualities, including an extensive surface area, versatile synthetic capabilities, adaptive structure, and other notable features.11–13
In recent decades, numerous novel porous materials have emerged and progressed, encompassing microporous, mesoporous, and macroporous structures. These materials consist of porous organic polymers (POPs), covalent–organic frameworks (COFs), and metal–organic frameworks (MOFs).14–17 Amidst the proliferation of recently developed materials, there has been a renewed scientific interest in POPs owing to their unique capacity to combine the properties of porous and polymeric substances. POPs are metal-free polymeric organic materials that are predominantly composed of complex molecular structures made up of lightweight elements including carbon, hydrogen, oxygen, nitrogen, and boron.18–20
In general, porous organic polymers (POPs) exhibit numerous structural and physicochemical benefits in comparison to conventional and modern porous materials.21 These benefits placed them at the vanguard of the forthcoming generation of multipurpose functional materials. POPs offer many advantages compared to traditional inorganic substances such as activated carbons, zeolites, etc. These advantages include a significant surface area, low density, and strong physicochemical durability. In addition, it is possible to incorporate functional components into POP structures via modifications that occur both before and after synthesis. The pre-synthetic methods offer an extensive range of chemical reactions and the adaptability of monomer design affords considerable potential for the modification of functionalities.22–24 On the other hand, post-synthetic modification functions as a potent mechanism to enhance the porous architecture's functional versatility. Redox switches are the most frequently observed molecular switch types in POPs.25,26 These switches are susceptible to alteration when the redox potential of their surroundings alters. A variety of applications of redox switches involve the removal of substances from the environment, such as dyes, iodine, and oxoanions. They are also utilized as electrochemical devices, drug delivery systems, actuators, and sensors.27–29 Different forms of 4,4′-bipyridine, often referred to as viologens, are specific types of redox molecular switches that have been the subject of extensive research. Owing to their positive charge, these switches are amenable to reversible reduction via chemical or electrical reduction methods to radical cationic or neutral species (Scheme 1).30–33 The incorporation of viologen moieties into polymeric frameworks to form viologen-based porous organic polymers (vPOPs) presents a multitude of benefits: (i) the radical cationic species remain in an unstable state for prolonged durations under ambient conditions as the extended polymeric structures stabilize the radicals. (ii) In applications that rely on the in situ generation of radical cationic species, polymeric viologens frequently demonstrate enhanced performance in comparison to monomers and dimers, owing to their improved charge transfer capabilities. (iii) The porosity of vPOPs makes them highly suitable for applications requiring significant surface areas, such as gas adsorption and separation, including reaction catalysis. (iv) The inherent cationic property of vPOPs facilitates the dispersion of insoluble substances. (v) The capacity to regulate the redox state of their viologen moieties enables vPOPs to recognize a variety of substances (such as hydrophobic, hydrophilic, anionic, cationic and other substances) selectively.34–40 In light of the exponential growth of scientific investigation and recognizing the promising possibilities of new materials, we present a thorough analysis that explores the current state and recent advancements in various categories of vPOPs used in the diverse environmental context. Their diverse functionalization techniques and synthetic strategies are given particular emphasis. As illustrated in Fig. 1, the review subsequently undertakes a comprehensive analysis of the pragmatic implementations of vPOPs in environmental remediation endeavours, including the storage/segregation of hazardous vapors, elimination of organic/inorganic contaminants, iodine adsorption, and energy storage/conversion. Especially, we shed light on the present obstacles, along with possible advantages, and prospects of these promising materials for energy and environmental remediation. To the best of our knowledge, this review is unique in terms of the application of ionic vPOPs for energy and environmental remediation.
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1) solvent mixture and the resulting mixture was then subjected to 2.45 GHz microwave irradiation for one hour at 100 °C in a 100 mL microwave reaction vessel. The outcome of this procedure was a sheet-like viscoelastic/gel organic framework (COGF). Following the completion of these reactions, the synthesized COGF was utilized to extract iodine in the cyclohexane phase in an efficient manner, as discussed later in the section I2 uptake. Furthermore, the aforementioned research group utilized microwave irradiation to incorporate azacalix[4]arene, an organic macrocycle, into the structure of a viologen-based covalent organic framework (ACA-COF).44 The ACA-COF has been utilized in the adsorption of uric acid and creatinine, which are critical byproducts produced during hemodialysis in patients suffering from renal failure. The detailed reports of other microwave-synthesized vPOPs are presented in Table 1.
| S. no. | vPOPs | Methods for synthesis of vPOPs | Name reactions for the synthesis of vPOPs | Reaction conditions | Ref. |
|---|---|---|---|---|---|
| T1.1 | COGF | Microwave | Zincke reaction | EtOH : H2O (1 : 1), 100 °C, 2 h |
43 |
| T1.2 | COP1++ | Microwave | Menshutkin reaction | MeCN, 89 °C, 1 h | 59 |
| T1.3 | ACA-COF | Microwave | Zincke reaction | EtOH : H2O (1 : 1), 100 °C, 2 h |
44 |
| T1.4 | TFAM-BDNP | Microwave | Zincke reaction | EtOH : H2O (4 : 1), 100 °C, 2 h |
67 |
| T1.5 | PV-COF | Microwave | Zincke reaction | EtOH : H2O (1 : 1), 100 °C, 2 h |
82 |
| T1.6 | CONs | Solvothermal | Zincke reaction | EtOH : H2O (1 : 1), 120 °C, 72 h |
89 |
| T1.7 | COTs | Solvothermal | Zincke reaction | EtOH : H2O (1 : 1), 120 °C, 72 h |
89 |
| T1.8 | cCTN:Cl− | Solvothermal | Zincke reaction | MeCN : H2O (10 : 1), 120 °C, 72 h |
45 |
| T1.9 | HS | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 120 °C, 72 h |
43 |
| T1.10 | HT | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 120 °C, 72 h |
|
| T1.11 | Compound-1 | Solvothermal | Zincke reaction | 1,4-Dioxane : EtOH : chlorobenzene (1 : 1 : 1), 120 °C, 72 h |
46 |
| T1.12 | V-PCIF-X | Solvothermal | Zincke reaction | DMF, 180 °C, 48 h | 78 |
| T1.13 | VBCOP | Solvothermal | Zincke reaction | MeOH : dioxane (1 : 1), 120 °C, 72 h |
65 |
| T1.14 | TZ-PAF | Solvothermal | Zincke reaction | THF : H2O (1 : 1), 100 °C, 72 h |
66 |
| T1.15 | PC-COF | Solvothermal | Zincke reaction | AcOH : EtOH : H2O, 100 °C, 168 h |
60 |
| T1.16 | vGC | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 120 °C, 72 h |
80 |
| T1.17 | vGAC | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 120 °C, 72 h |
|
| T1.18 | vMEL | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 120 °C, 72 h |
|
| T1.19 | vBPDP | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 120 °C, 72 h |
|
| T1.20 | VIP-X | Solvothermal | Menshutkin reaction | MeCN, 100 °C, 48 h | 88 |
| T1.21 | Por(Co)-Vg-COF | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 90 °C, 72 h |
84 |
| T1.22 | IISERP-POF9 | Solvothermal | Bakelite bond formation | Dioxane : THF, 200 °C, 72 h |
83 |
| T1.23 | IISERP-POF9 | Solvothermal | Bakelite bond formation | Dioxane: THF, 200 °C, 72 h |
83 |
| T1.24 | IISERP-POF9 | Solvothermal | Bakelite bond formation | Dioxane : THF, 200 °C, 72 h |
|
| T1.25 | AN-POP | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 120 °C, 72 h |
85 |
| T1.26 | BD-POP | Solvothermal | Zincke reaction | EtOH : H2O (4 : 1), 120 °C, 72 h |
|
| T1.27 | SCU-COF-1 | Solvothermal | Schiff base reaction |
o-DCB : BuOH : acetic acid (19 : 1 : 2), 120 °C, 144 h |
86 |
| T1.28 | TpVCB[7] | Room temperature | Schiff base reaction | DCM : H2O, 72 h |
48 |
| T1.29 | V2DP | Room temperature | Schiff base reaction | TfOH, 144 h | 47 |
| T1.30 | RT-iCOF | Room temperature | Schiff base reaction |
o-DCB : BuOH (7 : 3), 24 h |
87 |
| T1.31 | IPOP | Solvothermal | Menshutkin reaction | MeCN, 90 °C, 72 h | 102 |
| T1.32 | VCR-POP-1 | Solvothermal | Knoevenagel condensation | DMSO, CS2CO3, 120 °C, 72 h | 110 |
The increasing demand of a growing human population, coupled with accelerated industrial development and global environmental issues, has profoundly affected the availability of clean water for civilization, leading to serious problems such as water shortages and mounting water pollution. Water pollution has become a major worldwide problem, and the preservation of micro contaminants in water has drawn a significant deal of scientific attention.52,53 Several sustained enhanced chemical separation technologies have been employed or are being tested to decontaminate clogged water systems, including effluent and salt water, to provide a fresh and pure water supply. Of these, adsorption-based purification technologies have been acknowledged as feasible and eco-friendly alternatives to conventional treatments, which may be attributable to their exceptional efficiency, effortless operation, and cost-effectiveness. Significant progress has been made in developing very effective adsorbents for separation methods that rely on sorption in the last several years.54,55 In the field of pollutant removal from water and wastewater treatment, vPOPs have been regarded as highly promising absorbent substances because of their distinctive properties such as redox activity, tuneable pore diameter, free exchangeable anions and so on. Here, we have categorized pollutants into two classes, namely,: (i) organic pollutants and (ii) inorganic pollutants, and discussed the role of vPOPs in removing them from water thoroughly. Iodine removal from water and iodine capture through vPOPs are also subject to in-depth discussion.
In a recent exploration, Ghosh et al. delved into the potential of a vPOP (named iVOFm) to effectively eliminate several harmful anionic organic compounds, including pigments, antimicrobial agents, as well as inorganic pollutants (Fig. 2(a)).58 The study introduced a solid-state acid vapor-aided approach utilizing silica nanoparticles as templates for designing and synthesizing a macro-micro hierarchical iVOFm. The resulting iVOFm underwent thorough characterization, revealing unique features such as a cationic backbone with densely distributed free counter anions, hierarchical porosity at macro and micro scales, and exceptional chemical stability. Notably, the size and quantity of macropores in iVOFm could be easily adjusted using an appropriate SiO2 nanoparticle template. Here, the customized design of iVOFm employs a synergistic approach, integrating electrostatically induced ion exchange processes, macro-micro pores, and specialized binding sites, to efficiently target and remove the desired contaminants. The efficacy of iVOFm in removing organic dyes, specifically alizarin red S and methyl orange, and antibiotics such as sulfamethazine (SMT) and sulfadimethoxine (SDM) from water was assessed. iVOFm demonstrated swift adsorption capabilities for diverse organic toxins, iodine, and metal-based oxoanions, achieving a clearance efficiency exceeding 93% within 30 s (Fig. 2(b) and (c)). The research further illustrated the successful removal of the antibiotic SDM from water, highlighting a rapid sorption capacity that maintained high effectiveness even in the presence of coexisting anions such as nitrates, chloride, and bromide. The investigation suggested that the exceptional pollutant-trapping efficiency could be attributed to the rapid diffusion of pollutants facilitated by well-structured and interconnected macropores, synergistically interacting with the cationic backbone.
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| Fig. 2 (a) Synthetic route for iVOFm. (b) and (c) Removal kinetics and % removal of all pollutants through iVOFm. Reproduced with permission from ref. 58. Copyright 2022 Wiley-VCH. (d) Schematic representation of the synthesis of COP++1. (e) Bar graphs of adsorption capacities of the cationic, radical-cationic and neutral forms of COP1 for fluorescein, rhodamine B, and Nile Red. Reproduced with permission from ref. 59. Copyright 2014 the Royal Society of Chemistry. | ||
Simultaneously, a comprehensive investigation was carried out to assess how the redox state of the viologen moieties of vPOPs influences the capture of hydrophilic and hydrophobic dyes. Trabolsi et al. synthesized a new type of phosphazene based vPOP (COP1), for the absorption of neutral fluorescein dye (hydrophilic), cationic rhodamine B dye (hydrophilic), and anionic Nile red dye (hydrophobic) (Fig. 2(d)). The study revealed that both the charge and the level of hydrophilic or hydrophobic nature of both the absorbent and the dye play a crucial role in determining the absorption capacity. Efficient adsorption of fluorescein by the dicationic COP++1 was observed, achieving a remarkable removal rate of 99% in just 4 minutes (Fig. 2(e)).59 This high efficiency can be attributed to robust hydrophilic–hydrophilic associations, which are not feasible between fluorescein and radical cationic (
) or neutral (COP01) vPOPs. Similarly, the neutral COP01 demonstrated significant capability, eliminating approximately 85% of Nile red within an hour. The effectiveness of this removal is likely due to the potential occurrence of hydrophobic interactions between the COP01 and Nile red. Dicationic (COP++1) and radical cationic (
) conjugated organic polymers displayed a maximum removal efficiency of 25% for Nile red. The study's findings suggest that the specificity of vPOPs may be customized for a particular pollutant by altering the redox phase of the viologen moiety. Li et al. explained these anionic dye adsorption phenomena through viologen-based cationic POPs (PC-COF) by the concept of soft and hard acid–base theorem (Fig. 3(a)).60 Anionic dyes are generally considered as soft bases, which will be paired up with viologen-based POPs, and act as soft acids, whereas the Cl− anions are considered as hard bases, paired up with cations from dye considered as hard acids. They synthesized crystalline imine-based vPOPs (PC-COF) and further conducted adsorption studies, examining a range of anionic dyes such as acid green, acid red 27, indigo carmine, methyl orange, and Direct Fast Brown M. Remarkably, this material demonstrated an uptake exceeding 97% for these diverse dyes even at very low concentrations (Fig. 3(b)). The authors attribute the enhanced absorption capacity to the implementation of the hard and soft acid/base approach. In this context, anionic dyes, serving as soft bases, create pairs with the softly acidic vPOPs (PC-COF), while hard Cl− ions form pairs with hard Na+ ions and these lead to efficient adsorption of toxic dyes. Several vPOPs are reported for this particular removal study, which are documented in Table 2.
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| Fig. 3 (a) Schematic of the synthetic route for PC-COF. (b) The plots of absorbance of dyes by PC-COF versus concentration of the dyes in water. Reproduced with permission from ref. 60. Copyright 2014 the Royal Society of Chemistry. (c) Synthetic strategy for ACA-COF through the Zincke reaction. (d) Removal percentage (%) of uric acid and creatinine via ACA-COF. Reproduced with permission from ref. 44. Copyright 2022, American Chemical Society. | ||
| S. no. | Name of vPOPs | Organic dye | Organic dye capture capacity (mg g−1) | Equilibrium times | Cycle | Ref. |
|---|---|---|---|---|---|---|
| T2.1 | iVOFm | Alzarine red S | — | 5 min | — | 58 |
| Methyl orange | — | 5 min | — | |||
| T2.2 | COP++1 | Fluorescein | — | 4 min | — | 59 |
| T2.3 |
|
Rhodamine B | — | 60 min | ||
| T2.4 | COP01 | Nile red | — | 60 min | ||
| T2.5 | COP++1 | Congo red | 928 mg g−1 | 15 min | — | 69 |
| T2.6 | C-NSANaphHCP@Br | Methyl orange | 1010 mg g−1 | 60 min | 5 | 90 |
| T2.7 | QUST-iPOP-1 | Congo red | 1074.9 mg g−1 | 90 min | — | 92 |
| Methyl orange | 300 mg g−1 | 90 min | — | |||
| T2.8 | V-CDP | Congo red | 323 mg g−1 | 425 min | 5 | 94 |
| Methyl orange | 370 mg g−1 | 425 min | 5 |
The recent advancement of research has led to the utilization of these vPOPs in the adsorption of uric acid and creatinine which are present in water used for dialysis. Trabolsi et al.44 synthesized an azacalix[4] arene-based vPOP (ACA-COF) under microwave irradiation (Fig. 3(c)).44 This is an exceptional instance where a synthetic approach is used to chemically modify an organic macrocycle to limit its ability to change shape and create an ordered substance. The ACA-COF was further used for the removal of uric acid and creatinine from dialyzed water. This application has the capability to save 400 L of water per patient per week. Although it has just gained recognition in the last decade, it has the potential to successfully tackle the issue of water shortage in arid regions worldwide. Their COF exhibited very fast adsorption rates, surpassing previously documented values by many orders of magnitude (Fig. 3(d)).
| S. no. | Name of vPOPs | Kinetic study | Oxoanion capture capacity (mg g−1) | Selectivity | Ref. | |
|---|---|---|---|---|---|---|
| Time for oxoanion removal | % of oxoanion removal | |||||
| Cr2O72− removal | ||||||
| T3a.1 | C-NSANaphHCP@Br | 60 min | 95% | 745 | F−, Cl−, Br−, ClO3− NO3, CO32− and PO43− | 90 |
| T3a.2. | IISERP-POF9 | 60 min | 77% | 128.10 | Cl−, ClO4−, and SO42− | 83 |
| T3a.3. | IISERP-POF10 | 60 min | 78% | 125.21 | Cl−, ClO4−, and SO42− | |
| T3a.4. | IISERP-POF11 | 60 min | 81% | 131.22 | Cl−, ClO4−, and SO42− | |
| T3a.5. | COP++1 | 15 min | 95% | — | — | 70 |
| T3a.6. | CON-1 | 60 min | 98% | 293 | — | 93 |
| CrO42− removal | ||||||
| T3b.1. | Compound-1 | 30 min | 98.25% | 133 | Cl−, NO3−, Br−, SO42− | 46 |
| T3b.2. | iCOF-2 | 60 min | 99% | 253 | Cl−, NO3−, Br−, SO42− | 91 |
| MnO4− removal | ||||||
| T3c.1 | Compound-1 | 5 min | 99.9% | 297.3 | Cl−, NO3−, Br−, SO42− | 46 |
| T3c.2 | IISERP-POF9 | 60 min | 99% | 110.53 | Cl−, ClO4−, and SO42− | 83 |
| T3c.3 | IISERP-POF10 | 60 min | 97% | 103.11 | Cl−, ClO4−, and SO42− | |
| T3c.4 | IISERP-POF11 | 60 min | 98% | 113.81 | Cl−, ClO4−, and SO42− | |
| T3c.5 | iVOFm | 30 s | 99% | — | — | 58 |
| T3c.6 | COP++1 | <1 min | 99% | — | — | 70 |
| T3c.7 | iCOF-2 | 60 min | 99% | 334 | Cl−, NO3−, Br−, SO42− | 91 |
| T3c.8 | QUST-iPOP-1 | 8 min | 99% | 514 | — | 92 |
| ReO4− removal | ||||||
| T3d.1 | Compound-1 | 60 min | >80% | 517 | Cl−, NO3−, Br−, SO42− | 46 |
| T3d.2 | TFPM-BDNP | 1 min | 90% | 998.26 | NO3−, SO42−, PO43−, CO32− | 67 |
| T3d.3 | TZ-PAF | — | — | 982 | NO3−, SO42−, Cl− H2PO4 | 66 |
| T3d.4 | VBCOP | 5 min | 98% | 444 | Cl−, NO3−, SO42− | 65 |
| T3d.5 | iVOFm | 30 s | 97% | — | — | 58 |
| T3d.6 | COP++1 | 30 min | 99% | — | — | 70 |
| T3d.7 | SCU-COF-1 | 1 min | 99% | 367 | NO3− and SO42− | 86 |
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| Fig. 4 (a) Schematic representation of the oxo-anion capture by compound-1. (b)–(g) Kinetic studies of removal of all oxoanions by compound-1. Reproduced with permission from ref. 46. Copyright 2014 the Royal Society of Chemistry. (h) Schematic representation of the synthesis of VBCOP. (I) Effect of contact time on the removal efficiency of Re(VII) by VBCOP (C0 = 45 mg L−1, pH = 7). (j) Effect of contact time on the removal efficiency of 99Tc(VII) by VBCOP. Reproduced with permission from ref. 65. Copyright 2018, Elsevier. (k) Schematic of the synthetic route for TZ-PAF. (l) and (m) Sorption kinetic investigations of TZ-PAF for ReO4− uptake. Reproduced with permission from ref. 66 Copyright 2018, Elsevier. (n) Synthetic pathway of 3D iCOF (TFAM-BDNP). (o) and (p) Adsorption kinetics and adsorption isotherm of TFAM-BDNP for ReO4− capture. Reproduced with permission from ref. 67. Copyright 2018, Elsevier. | ||
In a very recent report, the tetra aza macrocycle containing vPOP was considered as a very potential adsorbent material for separating TcO4− and ReO4− from wastewater. 99Tc is a radioactive element that releases beta particles. It has a significant fission output and a lengthy half-life. The prompt removal of 99Tc from liquefied radioactive waste is essential due to its intrinsic potential for causing harm to humans. On the other hand, Re is also considered as a carcinogenic material. In this report, Xia et al. synthesized a tetraaza macrocycle containing vPOP through the solvothermal-assisted Zincke reaction, named VBCOP (Fig. 4(h)).65 This material has great potential as an adsorbent for the absorption of ReO4−/TcO4−, demonstrating exceptional adsorption properties such as fast adsorption rate, high adsorption capacity, excellent selectivity, and efficient regeneration (Fig. 4(i) and (j)). This efficient adsorption process is primarily governed by ion-exchange mechanisms. In addition, they demonstrated the new sequestration of Re(IV) by including a malleable tetraaza macrocycle ligand inside the framework architecture for the first time. The use of EXAFS and XPS analysis reveals that VBCOP0 has the ability to create a compound with Re(IV), indicating its potential use in eliminating soluble low-valent Tc species from radioactive wastewater. In summary, VBCOP showed promise in effectively treating both high-valent and low-valent Tc in nuclear effluent. The same group reported a diamond-like topological vPOP named TZ-PAF, for efficient remediation of radioactive TcO4− from wastewater. TZ-PAF was solvothermally synthesized via the Zincke reaction (Fig. 4(k)).66
The TZ-PAF that was synthesized had exceptional resistance to acids and high thermal environment. The material showed rapid anion-exchange kinetics and a high capacity for adsorption (982 mg g−1 for ReO4−), which may be ascribed to its low-density structure and the presence of many cationic pyridinium rings that act as sites for anion exchange (Fig. 4(k)–(m)). In addition, TZ-PAF had the greatest capacity for removing TcO4−, with a Kd value of 5.02 × 106 mL g−1. It also exhibited exceptional reusability for extracting TcO4− from both extremely acidic media and low-activity wastewater streams. Hence, the dia-topology TZ-PAF has successfully addressed the drawbacks of vPOPs, including their susceptibility to acid damage and limited ability to absorb TcO4−/ReO4−. As a result, it has emerged as a promising option for efficiently and completely eliminating ReO4− from nuclear wastes. This paper presents a novel method for creating very stable sorbents, which are very efficient for TcO4− adsorption.
Qui et al. recently documented, for the first time, the synthesis of three-dimensional viologen-based covalent organic frameworks (Fig. 4(n)).67 They have successfully produced a novel 3D ionic covalent organic framework (iCOF), named TFAM-BDNP, through the microwave-assisted Zincke reaction. TFAM-BDNP demonstrates exceptionally rapid response times, a high adsorption rate, superior selectivity, and impressive resistance to changes in pH, along with the ability to be reused for the removal of TcO4−/ReO4−. Owing to its outstanding stability, open hydrophobic channels, and high charge density, TFAM-BDNP presents itself as a promising candidate for the removal of TcO4−/ReO4− (Fig. 4(o) and (p)). This research not only diversifies the structural variations of 3D covalent organic frameworks but also broadens their applications in processes related to the disposal of nuclear waste.
and COP2˙+) have the potential to engage in a series of reduction–oxidation reactions with polyiodides and formed dicationic vPOP and I3− (Fig. 5(h)) This process provides vPOPs a substantial ability for absorbing iodine vapor.69 The enduring nature of the radical cationic viologen is crucial for facilitating these reactions.
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| Fig. 5 (a) Synthesis of COP++1 and COP2++. (b) Real images of iodine vapor adsorption in COP1 and COP2 at 60 °C. (c) Iodine vapor capture capacities of COP1 and COP2 in three different redox states. (d) Schematic representation of anion removal (MnO4−, Cr2O72−) by anion exchange, where yellow spheres represent polymer particles (COP1 and COP2). Reproduced with permission from ref. 70. Copyright 2014 the Royal Society of Chemistry. (e) Synthesis of the hollow sphere (HS) and hollow tube (HT) via the solvothermal synthesis approach and the covalent organic gel framework (COGF) via the microwave synthesis approach. (f) Graph of % removal of I2 from a 1 mM solution in cyclohexane over time by HT, HS and COGF. Reproduced with permission from ref. 43. Copyright 2022, American Chemical Society. (g) Synthesis of COP++1 and COP2++. (h) Solution-phase iodine adsorption by the three redox states of COP1 and COP2. Reproduced with permission from ref. 69. Copyright 2022 Wiley-VCH. (i) Synthesis of CONs and COTs, (j) and (k) Iodine adsorption experiments. Reproduced with permission from ref. 89. Copyright 2022 Wiley-VCH. | ||
The above-mentioned discussion is a common overview of how the redox-active behaviour of vPOPs affected the iodine adsorption process. The 1st synthesized vPOPs gel (COGF), through the solvothermal assisted Zincke reaction, exhibited remarkable iodine adsorption efficiency (Fig. 5(e)).43 The same research group reported viologen and pyrene-based covalent organic nanosheets (CONs) and covalent organic tubes (COTs) for iodine adsorption in the solution phase as well as the vapor phase (Fig. 5(i)). COTs exhibited high efficiency in iodine adsorption in both phases, as the presence of triple bonds and more cationic surface leads to fast iodine capture in COTs (Fig. 5(j) and (k)).89
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| Fig. 6 (a) The synthesis of PCP-Cl, PCP-BF4 and PCP-PF6. CO2 and N2 uptake isotherms of PCPs measured up to 1 bar at (b) 273 K and (c) 298 K. Reproduced with permission from ref. 74. Copyright 2014 the Royal Society of Chemistry. (d) Synthesis route for cCTFs. CO2 adsorption isotherms of cCTFs at (e) 273 K, (f) 298 K, and (g) 323 K. (H) The isosteric heat of adsorption (Qst) plots for CO2. Reproduced with permission from ref. 75. Copyright 2022, American Chemical Society. | ||
| S. no. | vPOPs | BET surface area (SBET) m2 g−1 | CO2 uptake (mmol g−1) | Pressure (bar) | Ref. | ||
|---|---|---|---|---|---|---|---|
| 273 K | 298 K | 323 K | |||||
| T4.1 | cCTF-400 | 744 | 2.86 | 1.88 | 1.18 | 1 | 75 |
| T4.2 | cCTF-450 | 861 | 2.25 | 1.40 | 0.86 | 1 | |
| T4.3 | cCTF-500 | 1247 | 3.02 | 1.82 | 1.06 | 1 | |
| T4.4 | V-PCIF-Br | 174 | 1.97 | 1.41 | — | 1 | 78 |
| T4.5 | V-PCIF-Cl | 383 | 2.33 | 1.66 | — | 1 | |
| T4.7 | POP-V1 | 812 | — | 0.92 | — | 1.1 | 76 |
| T4.8 | Red-POP-V1 | 606 | — | 0.67 | — | 1.1 | |
| T4.9 | POP-V2 | 960 | — | 1.27 | — | 1.1 | |
| T4.10 | Red-POP-V2 | 591 | — | 1.09 | — | 1.1 | |
| T4.11 | PCP-Cl | 755 | 2.31 | 1.39 | — | 1 | 74 |
| T4.12 | PCP-BF4 | 586 | 2.20 | 1.32 | — | 1 | |
| T4.13 | PCP-PF6 | 433 | 1.77 | 1.06 | — | 1 | |
| T4.14 | CCTF-500 | 1353 | — | 1.94 | — | 1 | 73 |
| T4.15 | V-iPHPs | 562 | 1.24 | — | — | 1 | 78 |
| T4.16 | VIP-Br | 38 | — | — | — | — | 88 |
| T4.17 | VIP-Cl | 56 | — | — | — | — | 88 |
| T4.18 | H2-ICOP | 9 | 0.96 | 1.42 | 0.39 | 1 | 95 |
| T4.19 | Zn-ICOP | 20 | 0.45 | 0.89 | 0.54 | 1 | |
| T4.20 | SYSU-Zn@IL1 | 38 | 1.54 | 0.90 | — | 1 | 96 |
The incorporation of halogen bond donors (HBDs) in the frame of vPOPs leads to a new class of materials that can be used as a catalyst for CO2 fixation. Utilizing this new concept Chen et al. synthesized HBD-incorporated hybrid vPOPs, named V-iPHPs (Fig. 7(c)), and used these materials for catalytic CO2 fixation.77 V-iPHPs were synthesized through the solvothermal assisted Heck reaction. V-iPHPs have tunable surface areas and pore volumes, and adjustable ionic sites. They exhibit metal-free heterogeneous catalytic activities in CO2 fixation with diverse epoxide substrates under mild conditions (Fig. 7(d)). The catalyst's remarkable performance is credited to synergistic catalysis sites, ample mesoporosity, and the hydrophobic reaction microenvironment. Wang et al. also demonstrated that POSS and viologen-linked vPOPs (V-PCIF-X, X = Cl, Br) function as a metal-free catalyst and adsorbent of exceptional efficacy, enabling the concurrent capture and conversion of CO2 (Fig. 7(a)). Due to their high surface area, tunable pore size and specifically presence of mobile Si–OH, these vPOPs are remarkable CO2 adsorbents (Fig. 7(b)) and are denoted as excellent metal-free catalysts for the conversion of CO2.78
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| Fig. 7 (a) The synthesis of V-PCIF-X (X = Cl, Br), (b) CO2 uptake of V-PCIF-Cl and V-PCIF-Br at 273 K and 298 K. Reproduced with permission from ref. 78. Copyright 2014 the Royal Society of Chemistry. (c) Synthetic route for V-iPHP-1 and V-iPHP-2, (d) CO2 uptake of V-iPHP-1 and V-iPHP-2 at 273 K and 298 K. Reproduced with permission from ref. 77. Copyright 2022, American Chemical Society. | ||
Very recently our group reported a series of viologen-based covalent organic networks (vCONs) as metal-free bifunctional electrocatalysts for oxygen reduction reaction (ORR) and oxygen evolution reaction (OER).80
Here, we synthesized four vCONs through the solvothermal-assisted Zincke reaction, denoted as vGC, vGAC, vMEL and vBPDP, based on triamines used as reactants (Fig. 8(a)). The incorporation of redox-active viologen groups into the extended covalent organic framework was essential for achieving exceptional stability in both acidic and basic environments, as well as for demonstrating dual functionality in the oxygen reduction reaction (ORR) and oxygen evolution reaction (OER). The verification was conducted using cyclic voltammetry (CV) curves. Significantly, vBPDP exhibited a remarkable oxygen reduction reaction (ORR) efficiency, achieving a half-wave potential of 0.72 V relative to a reversible hydrogen electrode (RHE) in a 1 M KOH electrolyte (Fig. 8(b)–(e)). However, vMEL demonstrated impressive OER (oxygen evolution reaction) performance, achieving an overpotential of 320 mV at a current density of 10 mA cm−2 and a Tafel slope of 109.4 mV dec−1 in a 1 M KOH electrolyte solution (Fig. 8(f) and (g)). This research is notable for using unadulterated viologen-based covalent organic networks as bifunctional electrocatalysts (for ORR and OER) without the inclusion of any metallic elements or conductive substances. There is a firm conviction that these particular varieties of vCONs possess the capability and efficiency to function as bifunctional electrocatalysts for ORR and OER. Consequently, these vCONs will be extremely useful in energy storage devices of the upcoming generation.
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| Fig. 8 (a) Synthesis of vGC, vGAC, vMEL and vBPDP. (b) LSV curves of all vCONs. (c) K–L plot of vBPDP. (d) Methanol stability of vBPDP. (e) EIS spectra of all vCONs. (f) LSV curves for the OER of all vCONs. (g) Tafel plots of all vCONs. Reproduced with permission from ref. 80. Copyright 2014 the Royal Society of Chemistry. | ||
Wen et al. have effectively synthesized a two-dimensional redox-active cationic covalent triazine network (cCTN) utilizing the solvothermal-assisted Zincke reaction.45 This network acts as a metal-free electrocatalyst for ORR in order to generate H2O2 (Fig. 9(a)). The cCTN electrocatalyst was synthesized with a mesoporous structure, characterized by a pore width ranging from 2 to 10 nm. It has a total nitrogen concentration of 13.3 wt%. This polymer has a reversible two-electron redox mechanism, which is thought to enhance the ORR efficiency for the generation of H2O2. The cCTN electrocatalyst exhibits excellent ORR performance and impressive specificity (over 85%) for H2O2 production across a broad potential range (0.1–0.7 V) (Fig. 9(b)–(e)). Electron paramagnetic resonance (EPR) tests showed that the viologen units in the cCTN electrocatalysts may initiate the activation of molecular oxygen, resulting in the production of superoxide radicals (O2−), which support the 2e− pathway of the ORR for the electrochemical synthesis of H2O2. This work presents a novel method for developing metal free electrocatalysts that are extremely specific to producing H2O2 from O2. Current research is dedicated to improving the efficiency and specificity of the cCTN electrocatalyst.
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| Fig. 9 (a) Synthesis of cCTN:Cl−, (b) CVs of cCTN:Cl−, (c) CV of cCTN:Cl− in 0.1 M KOH solution, (d) LSVs of the ORR of cCTN:Cl−, and (e) Koutecky–Levich plots at different potentials. Reproduced with permission from ref. 45. Copyright 2014 the Royal Society of Chemistry. (f) Proposed mechanism of TpVXs, electrochemical characterization of TpVXs as cathode materials. (g) CV curves of TpVXs, (h) charge/discharge curves at indicated current densities of TpVXs, and (i) rate performance and (j) cycling stability of TpVXs cathodes. Reproduced with permission from ref. 81. Copyright 2022 Wiley-VCH. (k) Synthesis of the V2DP film. Electrochemical characterization of the V2DP film. (l) CV curves of the V2DP electrode at different scan rates from 10 to 100 mV s−1. (m) Real time images of reversible color changing of the V2DP film. (n) Schematic presentation of the in situ spectroelectrochemical measurement. UV-vis spectral changes of the V2DP electrode recorded during (o) reductive and (p) oxidative processes. Reproduced with permission from ref. 47. Copyright 2022 Wiley-VCH. | ||
These ionic vPOPs are also recognized as remarkable cathode materials for Li-ion batteries. Recently, Li et al. reported a series of novel cationic vPOPs, denoted as TpVXs (where X = Cl, Br, or I), used as cathode materials in Li-ion batteries (Fig. 9(f)). Halogens which are used in LI-ion batteries serve as efficient cathodic materials but exhibit significantly very poor cycling efficacy.81 The vPOPs (TpVXs) are specifically engineered to feature numerous pores and ionic redox-active components to effectively and durably trap halogen anions accurately and appropriately. The TpVBr and TpVI electrodes demonstrate a notable initial specific capacity of 116 and 132 mA h g−1 at 0.2C, respectively, along with an elevated discharge voltage of around 3.0 V (Fig. 9(g)–(i)). Remarkably, due to their permeable and ionic composition, TpVBr and TpVI exhibit exceptional durability over extended periods of use (86% and 98% capacity preservation after 600 cycles at 0.5C), surpassing the performance of the most advanced halogen electrodes (Fig. 9(j)).81
Viologens recognized as a crucial optoelectronic material have found application in solar cells either as the active chromophore or as materials modified for electrodes. Feng et al. showcase a highly crystalline 2D polymer film with immobilized viologen (V2DP),47 characterized by a dense array of inherent pores and well-defined channels that facilitate the efficient utilization of viologen moieties and ion transport (Fig. 9(k)). Leveraging this, they constructed V2DP-based electrochromic devices (ECDs) demonstrating swift switching speeds (2.8 s for coloration, 1.2 s for bleaching), a high Coulombic efficiency (989 cm2 C−1 at 90% of the full switch), and low energy consumption (21.1 μW cm−2) (Fig. 9(l)–(n)). Additionally, the researchers illustrated the integration of these ECDs with transparent solar cells (TSCs), creating energy-efficient electrochromic window systems capable of dynamically adjusting light automatically (Fig. 9(o) and (p)). This innovation aligns with intelligent solar spectrum management. Their findings lay the foundation for designing and synthesizing electroactive 2D polymer films for superior smart windows, broadening the possibilities for energy-efficient building applications in the future.
In the year of 2019, Li et al. reported an exceptionally stable vPOP, known as bipy-POP (Fig. 10(a)), which was synthesized by reacting 4,4′-bipyridine with tetrakis(4-(bromomethyl)phenyl)methane in N-methylpyrrolidone at a temperature of 110 °C and which was further employed as a heterogeneous catalyst for the debromination coupling reaction.101 The bipy-POP catalyst has shown significant efficacy in facilitating the reductive debromination of several benzyl bromides in N,N-dimethylformamide, using dithionite as the reductive reagent. The reactions preferentially produced dibenzyl sulfone derivatives for substrates that had an electron-donating group on the benzene ring (Fig. 10(b)). In general, the presence of an electron-withdrawing group on the benzene ring in substrates has been seen to result in the formation of coupling products, namely ethane derivatives. In some cases, substrates containing F, Cl, or CF3 were seen to have a preference for the production of sulfone derivatives. The study investigated the recyclability of bipy-POP in the catalysis of the reaction between (4-fluorophenyl) methyl bromide and diphenylmethyl bromide, resulting in the formation of sulfone or ethane derivatives. The results indicated that, even after 40 cycles of repeated use, the heterogeneous catalysis did not demonstrate a significant decrease in activity. Recently, a novel vPOP named IPOP was employed as a heterogeneous catalyst for the Michael addition of thiols to α,β-unsaturated carbonyl compounds (Fig. 10(c)).102 IPOP was synthesized through the Menshutkin reaction by using a twisted biaryl (TMBB) as the monomer (Fig. 10(c)). IPOP exhibits thermal stability and lacks solubility in water as well as in commonly used organic solvents such as MeOH, MeCN, EtOH, DCM, and others. IPOP has capabilities similar to the phase-transfer quaternary ammonium salt tetra-n-butylammonium bromide (TBAB), due to the inclusion of cationic sites and counter bromide anions in its polymeric matrix. This characteristic enables IPOP to be used as a reusable heterogeneous catalyst for organic transformations. IPOP is a very effective catalyst for the Michael addition of thiols to α,β-unsaturated carbonyl compounds (Fig. 10(d)). This process allows for the production of organosulfur compounds, namely b-arylthioketones, with high yields in isolation. Comparably, it has been demonstrated that IPOP can serve as a recyclable heterogeneous catalyst for the easy production of biscoumarins. These compounds belong to a significant category of molecular systems that demonstrate diverse biological properties, including anti-coagulant, anti-anthelmintic, anti-HIV, anti-bacterial, anti-oxidant, anti-cancer, and so on. Therefore, a new, effective, and environmentally friendly method has been created to synthesize b-arylthioketones and biscoumarins by imitating the phase transfer of quaternary ammonium salts. IPOP can be used as a heterogeneous catalyst for a minimum of 10 catalytic cycles without any decrease in catalytic activity.
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| Fig. 10 (a) Synthesis of bipy-POP, (b) catalyst bipy-POP used for debromination coupling reaction for formation of sulfone. Reproduced with permission from ref. 101. Copyright 2022 Wiley-VCH. (c) Synthesis of IPOP, (d) IPOP-catalysed Michael addition of thiols to a,b-unsaturated carbonyl compounds. Reproduced with permission from ref. 102. Copyright 2018, Elsevier. (e) Schematic diagram of the synthesis route for HVPOP-Cl, (f) performance of comparative materials in the cycloaddition of CO2. Reproduced with permission from ref. 103. Copyright 2014 the Royal Society of Chemistry. | ||
It has also been reported that vPOPs can play a direct catalytic role in fixing CO2 into cyclic carbonates from a variety of epoxide-starting materials. The mechanisms by which these reactions occur are as follows: at the very first step, the epoxide is activated via hydrogen bonding with the α-protons of viologen and the epoxide ring is then exposed by a nucleophilic attack of Cl− ions. The resulting intermediate undergoes recyclization upon reaction with CO2, whereas Cl− functions as a leaving group.72 Based on this mechanism, using the Sonogashira–Hagihara cross-coupling reaction, a viologen-based porous organic polymer featuring a hollow structure and active anions was synthesized (named VPOP-Cl) from two basic monomers (Fig. 10(e)).103 This material exhibited exceptional performance in the catalytic cycloaddition of CO2. The pore properties of pristine VPOP-Cl were modified by alterations in micromorphology, and the exchange of anions enhanced its catalytic performance. Additionally, the modified HVPOP-Br demonstrated excellent reusability and catalytic performance in a solvent-free, metal-free reaction system devoid of cocatalysts. A substantial enhancement in the catalytic efficiency of CO2 cycloaddition was achieved through the modification of the microscopic structure and the exchange of anions (Fig. 10(f)). This approach may offer suggestions for enhancing the catalytic performance of POPs utilizing polymers with a basic structure. Similarly, Chen et al. reported a series of crystalline vPOPs (designated VIP-X, X = Cl or Br) that have acted as the metal-free heterogeneous catalyst for the degradation of CO2. In the synthesis of cyclic carbonate via CO2 cycloaddition with epichlorohydrin at atmospheric pressure (1 bar) and a low temperature (40 °C), the optimal catalyst VIP-Br produced a high yield of 99%.88 Furthermore, under mild conditions, other diverse epoxides could also be converted into cyclic carbonates. Additionally, the catalyst VIP-Br exhibited favorable stability and could be readily isolated for reuse. The exceptional catalytic performance may be ascribed to the synergistic influence of the enriched bromine anion species and the accessible hydroxyl (OH) groups that originate from water molecules that are H-bonded. The same group reported HBD-incorporated hybrid vPOPs, named V-iPHPs (Fig. 7(c)), that were used for catalytic CO2 fixation.77 The V-iPHP-1 catalyst has exceptional metal-free heterogeneous catalytic properties in the process of CO2 fixation using various epoxide substrates, even under very gentle circumstances. Moreover, the heterogeneous catalyst V-iPHP-1 exhibits a high degree of recoverability and impressive reusability. The exceptional catalytic performance may be attributed to the synergistic catalytic effects resulting from the presence of hydrogen bond donors, namely Si–OH groups and Br− anions, as well as the abundance of mesopores and the hydrophobic reaction microenvironment.
560 μmol h−1 g−1, utilizing 10 mg COFs) along with a high apparent quantum efficiency (AQE) of 6.93% (Fig. 11(b) and (c)). Moreover, these exceptional results persisted throughout a 48 h photocatalytic cycle, surpassing the performance of the COF/ETM mixture system. Their approach was to maximize the utilization of 2D COFs, as a customizable platform utilized to incorporate various fundamental functions and improve photocatalytic performance synergistically via predesigned ordering frameworks.
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| Fig. 11 (a) Schematic diagram of the dual-module COF (System I) and the mixture of single-module COF with unembedded ETM (System II). (b) The hydrogen evolution test of the integrated Tp-2C/BPy2+-COF (19.10%) and the bare Tp–BPy–COF mixed with additional 2C/BPy2+ used as an ETM under visible-light irradiation. The orange integral area roughly reflects the hydrogen evolution difference between the two photocatalytic systems. (c) HERs of Tp-2CPBy2+-COF (10 mg) with different quaternization conversions. Reproduced with permission from ref. 107. Copyright 2022 Wiley-VCH. (d) Schematic representation of photocatalytic oxidative coupling of benzylamine through VCR-POP-1. (e) Photocatalytic performance in white-light-driven photocatalytic oxidative coupling of benzylamine into imine over different catalysts VCR-POP-1, VIL-CN, and V-POP-1. Reproduced with permission from ref. 110. Copyright 2022, American Chemical Society. (f) Schematic representation of TPCBP X–COF [X = ethyl (E), butyl (B), and hexyl (H)] structures. (g) Photocatalytic hydrogen evolution activities of TPCBP X-COFs. (h) pH effect of TEOA. (i) Photocatalytic stability test of TPCBP X–COFs. Reproduced with permission from ref. 108. Copyright 2022, American Chemical Society. | ||
Recently, Koyuncu and co-workers reported novel vPOPs [(TPCBP X-COF) [X = ethyl (E), butyl (B), and hexyl (H)]] where the frameworks containing a viologen moiety act as an acceptor structure and a biphenyl-bridged dicarbazole acts as an electroactive donor skeleton (Fig. 11(f)).109 Further, TPCBP X-COF is used as a photocatalyst for the photocatalytic HER. When subjected to visible light illumination for a duration of 8 h, the H2 evolution rate of the TPCBP B-COF (12.276 mmol g−1) is 2.15 and 2.38 times greater than that of the TPCBP H-COF (5.697 mmol h−1) and TPCBP E-COF (5.165 mmol h−1), respectively (Fig. 11(g)). The TPCBP B-COF structure is regarded as one of the most effective catalysts described in the literature for photocatalytic HER; it generates 1.029 mmol g−1 h−1 of hydrogen and has an apparent quantum capacity of 79.69% at 470 nm (Fig. 11(h) and (i)). This approach offers fresh perspectives on the development of innovative vCOFs for the future evolution of metal-free hydrogen through solar energy conversion.
vPOPs were also considered as a remarkable heterogeneous photocatalyst for the coupling reaction but this area of research is explored very rarely. Very recently, Chen et al. reported radical cationic vPOPs (named VCR-POPs) which are intended to facilitate metal-free photoredox catalysis of oxidative coupling of amines in the presence of visible light (Fig. 11(d)). These acetonitrile-based radical cationic vPOPs (VCR-POPs) are synthesized through a one-pot Knoevenagel condensation reaction involving 1,3,5-tris(p-formylphenyl)benzene and an acetonitrile-functionalized viologen-based ionic monomer (VIL-CN). It is noteworthy that the VCR-POPs obtained a stable viologen cationic radical, which likely underwent in situ single-electron reduction of the dicationic monomer VIL-CN during the Knoevenagel condensation reaction facilitated by the base catalyst Cs2CO3. The electron paramagnetic resonance spectrum and X-ray photoelectron spectroscopy were employed to validate the radical nature of the prototypical porous organic polymer VCR-POP-1. Compared to the ionic monomer VIL-CN, the optical and electrochemical properties of VCR-POP-1 demonstrate its semiconductor nature, exceptional light-harvesting capability, and enhanced charge separation and transfer efficiency due to its well-designed cationic radical polymer structure (Fig. 11(e)). Hence, by virtue of the predominant reactive oxygen species of singlet oxygen, the polymer VCR-POP-1 featuring π-conjugated structures and viologen-based cationic radicals may be considered a metal-free heterogeneous photocatalyst that exhibits exceptional efficiency in facilitating the oxidative coupling of amines in air driven by visible light.
The strategies employed for the synthesis of vPOPs are antiquated and devoid of progress in this domain. The majority of crystalline vPOPs were synthesized through the microwave method. However, solvothermal or room temperature synthetic approaches ended up with amorphous or semi-crystalline vPOPs. Surprisingly, synthesis of vPOPs at room temperature is very rare and less attempted. Room temperature synthesis offers several advantages over solvothermal synthesis or microwave synthesis. Synthesizing crystalline vPOPs at room temperature is a significant challenge as the reaction follows sluggish kinetics of crystallization. Therefore, researchers should explore innovative strategies, such as the use of tailored molecular precursors or novel templating agents, to overcome these barriers and develop efficient room-temperature synthesis protocols for crystalline vPOPs. Such advancements could revolutionize the field by enabling highly scalable and sustainable production of these materials for a wide range of applications.
We believe that significant studies have been achieved in energy and environmental remediation with the advent of vPOPs; however, there remain unresolved obstacles and challenges that necessitate attention. A significant obstacle is the presence of clogged surface regions on vPOPs, which arise from the occlusion of pores by counter anions. This occlusion hinders the uniform distribution of active sites with the desired porosity. To address these challenges, it is strongly encouraged that researchers prioritize template synthesis of vPOPs to achieve surface and pore size homogeneity; synthesize template-assisted thin layers; or implement 3D architectures onto vPOPs to enhance the likelihood of achieving uniform pore distribution. Limited research has been conducted on hybrid materials and vPOPs such as the implementation of macrocycle inside the vPOPs, or metal composite vPOPs, etc. Integrating viologens and other functional molecules into polymers holds significant promise and can significantly expand the range of applications for materials based on viologens. Fine-tuning mechanical properties through the selection of axle and macrocycle structures could yield valuable insights for optimizing applications, such as the utilization of resilient materials in flow experiments to remove pollutants through membranes. Presently, researchers have focused predominantly on the synthesis of vPOPs at laboratory-based small scale and showcasing their application in different directions. However, vPOPs exhibit immense potential for industrial-scale applications due to their unique combination of properties, including redox molecular switches and chemical stability. These materials offer solutions to a wide range of challenges in sectors such as gas storage, separation, catalysis, wastewater treatment, etc. In the future, transitioning vPOPs from laboratory-scale synthesis to industrial production could revolutionize various industries by providing efficient and cost-effective solutions. Scaling up production processes requires addressing challenges related to reproducibility, scalability, and cost-effectiveness. However, with continued research and development efforts, along with advancements in synthesis methodologies and manufacturing techniques, vPOPs have the opportunity to make a significant impact on industrial processes, leading to sustainable and innovative solutions for energy and environmental remediation. Regarding this matter, vPOPs’ structures can be strategically designed when particular applications are identified by analysing the correlations between functionality, performance, and pore structure. Notwithstanding these obstacles, the immense capacity of vPOPs as adsorbents and catalysts is substantial in terms of environmental remediation and energy conversion, and will likely inspire additional developments in structural chemistry and practical implementations. The unique coordinated sites, donor–acceptor structure, and electrostatic interactions within vPOPs make them a promising framework for resource recycling and energy conversion.
| EtOH | Ethanol |
| MeOH | Methanol |
| DCM | Dichloromethane |
| DMF | N,N′-dimethylformamide |
| MeCN | Acetonitrile |
| THF | Tetrahydrofuran |
| AcOH | Acetic acid |
| BuOH | Butanol |
| o-DCB | Ortho dichlorobenzene |
| This journal is © The Royal Society of Chemistry 2024 |