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Synthesis, characterization, thermal stability, and application of microporous hyper cross-linked polyphosphazenes with naphthylamine group for CO2 uptake

  • Amin Abid , Shahid Nazeer , Laraib Kiran , Saqlain Raza , Ikram Ahmad , Hafiz Tariq Masood , Ammar M. Tighezza , Sana Shahzadi , Muhammad Ramzan Khawar , Moonwoo La EMAIL logo and Dongwhi Choi EMAIL logo
Published/Copyright: June 21, 2024
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Abstract

There are numerous problems in the world, but environmental pollution is the biggest threat to life. Air pollution is the most critical form of environmental pollution because air is the most essential need of life. However, industrialization, population growth, and fossil fuel use increase hazardous and greenhouse gas concentrations daily. Greenhouse gases like carbon dioxide (CO2) contribute to global warming; hence, efficient, inexpensive, sustainable, and ecologically friendly air purification solutions are required. This study proposed a new method for synthesizing N- and P-rich polyphosphazene-based hyper cross-linked polymer (HCP) for CO2 adsorption. Due to their persistent porosity, low density, and high surface area, hyper cross-linked porous organic–inorganic hybrid phosphorus and nitrogen-rich polymers are cost-effective and promising gas adsorption materials. We synthesized hybrid organic and inorganic polyphosphazenes with nitrogen and phosphorus backbones and aromatic side groups cross-linked by the Friedel–Crafts alkylation process. HCP-A and HCP-B were cross-linked phosphazene-based microporous hybrid organic–inorganic polymers. HCP-A and HCP-B were produced in two stages. Hexachlorocyclotriphosphazene reacts with 1-napthylamine to form naphthyl amino phosphazene, which is cross-linked under optimum conditions to make cyclic HCP-A. Phosphorous dichlorophosphazene reacts with 1-naphthylamine to form poly[bis(1-naphthylamino) phosphazene] and is cross-linked to form linear HCP-B. HCP-A and HCP-B porous networks were studied with Brunauer–Emmett–Teller surface areas of 170.89 and 492.03 m2 g−1 and narrow pore sizes of 0.8–1.18 nm. These polymers are promising CO2 adsorbents due to their easy and cost-effective production, thermal stability, surface area, and CO2 absorption capacity.

1 Introduction

Developing methods to clean the air is becoming the most difficult challenge for scientists to overcome. In spite of the fact that there is no life without clean air, the concentration of poisonous chemicals and greenhouse gases is increasing every day as a result of industrialization, population growth, and the usage of fossil fuels. As time goes on, the situation in emerging countries such as Pakistan, India, and Bangladesh, among others, continues to deteriorate. It is of the utmost importance to develop ways that are efficient, inexpensive, sustainable, and environmental friendly in order to purify air to develop methods that remove greenhouse gases from the environment [13]. Greenhouse gases, such as carbon dioxide (CO2), are a key contributor to the phenomenon of global warming. As a result of the tremendous increase in the concentration of CO2 in the atmosphere that has occurred since the beginning of the industrial revolution, the current level of CO2 in the atmosphere has surpassed 400 parts per million. One of the most significant greenhouse gases is CO2, which is responsible for the establishment of the greenhouse effect and gradually heats the earth by absorbing and emitting radiation in the infrared range. Therefore, the accumulation of CO2 in the atmosphere has irreversible implications, such as climate change, global warming, the melting of glaciers, ocean acidification, sea level rise, and so on, which have led to alarm on a global scale. Several different techniques for capturing CO2 are utilized, such as liquid solvent-based absorption, solid sorbent-based adsorption, membrane process, and cryogenic separation process, but the adsorption technique shows great potential for CO2 uptake. Therefore, we synthesized a hyper cross-linked polymer (HCP) based on polyphosphazenes, rich in both nitrogen and phosphorus, which was developed for the purpose of adsorbing CO2. Hyper cross-linked porous organic–inorganic hybrid phosphorus and nitrogen-rich polymers (HCPMPs) are gas adsorption materials that are cost-effective and promising due to their persistent porosity, low density, and high surface area [4,5].

Porosity is a property of a polymer that is characterized by the presence of pores within its structure and the ability to efficiently adsorb substances through these pores. Over the past few years, porous polymers have become increasingly significant, and they have a wide variety of uses among them. The reason for this is that they possess a high surface area, great porosity, a small pore size, and a strong packing [6,7]. Micro-porous materials, meso-porous materials, and macro-porous materials are classified according to their pore size. To be more specific, micro-porous materials have a pore diameter of less than 2 nm (d ≤ 2 nm), meso-porous materials have a pore diameter of 2–50 nm (d ≤ 50 nm), and macro-porous materials have a pore diameter of larger than 50 nm (d > 50 nm) [6]. It is possible for pores to be open, closed, cylindrical, slit-shaped, characterized by planar walls, organized, or disordered. Pores can also be open or closed. Crystalline materials, such as metal–organic frameworks (MOFs), have holes that are regular and organized in shape, whereas amorphous materials have pores that are interconnected and irregular in shape [8,9].

In addition, porous polymers can be found in several morphological forms, including zero-dimensional (0D) nanoparticles [10], two-dimensional (2D) membranes and hollow capsules [11], as well as three-dimensional (3D) monolithic blocks [11,12]. Porous materials can be categorized into different classifications, including hybrid porous materials, inorganic porous materials, and pure organic materials [1315]. MOFs are hybrid porous materials composed of both inorganic and organic constituents [1,13,14,1618]. Inorganic porous materials are entirely composed of inorganic substances [16]. Pure organic polymers (POPs) consist primarily of benzene rings. There exist six distinct categories of POPs [19]. HCPs are of utmost significance among them. HCPs refer to highly cross-linked porous polymers, as indicated in the literature [1,14,18,20]. The hydrophobic chromatography process was initially introduced by Davankov et al. in the early 1970s [21]. The researchers created them by employing a thorough process of post-crosslinking linear polystyrene (PS) chains [22]. Their achievement is accomplished through Friedel–Craft reactions, which entail the formation of structural connections between adjacent aromatic rings and the remaining chains, resulting in a much-expanded state [12,23].

Highly porous materials (HCPs) are the most effective method for purifying air because of their exceptional porosity and large surface area. Highly porous materials, such as HCPs, have been extensively utilized in recent years for various environmental applications. They not only store but also sequester hazardous gases such as CO2 [4]. HCPs are typically synthesized using three primary methods: After cross-linking the polymer precursors, the functional monomers undergo a direct single-step poly-condensation reaction. Additionally, cross-linking is achieved with the use of external cross-linkers. Hyper cross-linking is a method that creates numerous minuscule pores in polymers [24]. The presence of these pores leads to a significant increase in the surface area of the polymer, hence enhancing its reactivity. HCPs possess exceptional characteristics such as large surface areas, favorable porosity, low density, effective adsorption qualities, straightforward synthesis, cost-effectiveness, environmental friendliness, remarkable thermal and chemical stability, lightweight nature, and reusability [9]. The exceptional characteristics of HCPs, in comparison to conventional polymers, make them highly promising contenders for addressing both environmental pollution and energy issues. They possess numerous intriguing uses, including water treatment, gas storage, super-capacitors, sensing, catalysis, drug delivery, and chromatographic separations [12,13,20,25]. In recent decades, polyphosphazenes have garnered significant interest and have drawn researchers to investigate several uses, including thermal stability, gas adsorption capacity, energy storage, and medicinal applications [2629]. Currently, there is extensive research being conducted on the use of HCPs as adsorbents to decrease the concentration of CO2 in the environment. For instance, the capacity to capture CO2 was evaluated in several types of MOP networks. Yao et al. synthesized this HCP by cross-linking tetraphenylethylene utilizing FDA as a cross-linking agent and FeCl3 as a catalyst. The purpose of this HCP was to enhance the uptake of CO2 [2931].

HCPs possess a high surface area and include diverse functional groups, enabling them to effectively eliminate pollutants, particularly those of a biological, organic, and inorganic nature. This is due to their large surface area and the presence of functional group sites. HCP adsorbents with a hydrophobic surface exhibit high sorption capability for many compounds, including volatile organic components and organic contaminants. Nanoparticles of Davankov-type hyper cross-linked adsorbents with selective adsorption qualities were synthesized. The solid-phase microextraction method can utilize nanoparticles that are coated on the surface to effectively adsorb various organic contaminants, including alkanes and benzene molecules. The HCP-coated fibers were utilized for their adsorption capabilities and tested for their ability to adsorb polycyclic aromatic hydrocarbons from the air. The results obtained were quite satisfactory [32].

Yang et al. fabricated a porous polyphosphazene polymer by forming imine linkages using Schiff base condensation [33]. They synthesized cyclophosphazenes with aromatic side groups and cross-linked them using the well-established Friedel–Crafts procedure. The researcher then analyzed and described the heat stability of these compounds [34]. Wang et al. synthesized unique microspheres of N-doped porous carbon polyphosphazenes that incorporate oxygen and phosphorus, specifically designed for the purpose of adsorbing CO2 [35]. Abid et al. synthesized a cost-effective hybrid material by combining inorganic and organic components through a Friedel−Crafts reaction, resulting in the formation of hybrid coordination polymers with Lewis base sites. The researchers synthesized heteroatom-enriched precursors by performing nucleophilic substitution of hexachlorocyclotriphosphazene (HCCP) with 2-naphthol. Subsequently, the precursors were polymerized using Friedel−Crafts alkylation to obtain heteroatom-enriched cyclic phosphazene polymers (HCPs) with an increased content of phosphorus and nitrogen. These highly crystalline porous materials demonstrate a moderate ability to adsorb CO2 and iodine (I2) [16]. In recent years, there has been a growing interest in the development of porous materials, both organic and inorganic, that incorporate nitrogen and phosphorus. These materials, known as nitrogen- and phosphorus-rich microporous polymers, have attracted attention due to their unique characteristics such as large surface areas, nitrogen- and phosphorus-based molecular structures, low densities, and high chemical and thermal stability. These properties make them suitable for various applications in different fields [3,13,14,16,27,36].

2 Experimental section

2.1 Materials

1-Naphthylamine (monomer), formaldehyde dimethyl acetal (FDA) (cross-linker), dichloroethane (solvent), and ferric chloride (FeCl3) (catalyst) were obtained from Sigma Organics and used as received in their pure form. HCCP was purchased from Aldrich and used as received. Tetrahydrofuran (THF) (solvent) and n-hexane were also purchased from Sigma Organics, treated with molecular sieves, refluxed, and distilled under a nitrogen atmosphere, and then used in the experiment.

2.2 Synthesis of hyper cross-linked polyphosphazenes

2.2.1 Synthesis of HCP-A (cyclic)

Step 1. HCCP reaction with 1-naphthylamine (synthesis of naphthyl amino phosphazene [NAP])

About 5.31 g of 1-naphthylamine was dissolved in 20 ml THF and then added dropwise into a separate solution containing HCCP (0.2 g) in 20 ml THF. The reaction mixture was stirred and refluxed at 70°C for 48 h. The resultant solution was filtered, excess THF was removed by a rotatory evaporator, and the final product was precipitated in n-hexane and dried in the oven [2628]. Through the reaction of HCCP with 1-naphthylamine, the synthesis of polyphosphazenes that are rich in nitrogen and phosphorus is accomplished. This reaction involves the substitution of chlorine atoms in HCCP with amino groups derived from 1-naphthylamine. As a result, this procedure results in the formation of NAP molecules that contain a significant amount of nitrogen and phosphorus. The reaction scheme is shown in Figure 1.

Figure 1 
                     Synthesis of NAP.
Figure 1

Synthesis of NAP.

Step 2. Cross-linking of NAP

HCP-A was synthesized by the Friedel–Crafts alkylation reaction. NAP (0.1 g) was dissolved in 1,2-dichloroethane (5–7 ml) and dispersed well, then iron chloride (FeCl3) (0.2–0.3 g) was added, and FDA or dimethoxymethane (0.5 ml) was also added to the reaction flask and stirred with an initial temp of 45–50°C for 5 h and then temperature was raised at 80°C for 14 h. Finally, the product was filtered and washed repeatedly with methanol and THF until the color of the catalyst disappeared to obtain pure HCPs and then dried in an oven [28,37,38]. The reaction scheme is shown in Figure 2.

Figure 2 
                     Synthesis of HCP-A (HCCP+1-naphthylamine).
Figure 2

Synthesis of HCP-A (HCCP+1-naphthylamine).

2.2.2 Synthesis of HCP-B (linear)

Step 1. Reaction of phosphorous dichlorophosphazene (PDCP) with 1-naphthylamine (synthesis of poly[bis(1-naphthylamino)phosphazene] [PBNAP])

About 5.31 g of 1-naphthylamine was dissolved in 20 ml of THF and then added dropwise into a solution of PDCP (0.25 g) and THF (20 ml). The reaction mixture was stirred continuously and refluxed at 70°C for 48 h. The resultant solution was filtered, excess THF was removed by the rotatory evaporator, and the final product was precipitated in n-hexane and dried in the oven [2628]. The reaction scheme is shown in Figure 3.

Figure 3 
                     Synthesis of poly[bis(1-naphthylamino)]phosphazene.
Figure 3

Synthesis of poly[bis(1-naphthylamino)]phosphazene.

Step 2. Cross-linking procedure

HCP-B was synthesized by the Friedel–Crafts alkylation reaction of PBNAP. PBNAP (0.1 g) was dissolved in 1,2-dichloroethane (5–7 ml) and dispersed well, then iron chlorine (FeCl3) (0.2–0.3 g) was added, and FDA or dimethoxymethane (0.5 ml) was also added in a reaction flask and stirred continuously with an initial temperature of 45–50°C for 5 h and then the temperature was raised to 80°C for 14 h. Finally, the product was filtered, washed well with methanol, and dried in the oven. The obtained products were washed repeatedly with methanol and THF until the color of the catalyst disappeared to obtain pure HCPs [28,37,38]. The reaction scheme is shown in Figure 4.

The microporous hyper-crosslinked polyphosphazenes with naphthylamine groups for CO2 uptake appear to be an innovative approach to carbon capture. The incorporation of naphthylamine groups into microporous hyper-crosslinked polyphosphazenes represents a distinctive chemical design. The naphthylamine groups likely introduce specific interactions and binding sites for CO2 molecules, potentially enhancing the material’s selectivity and affinity for capturing CO2. Hyper-crosslinking often leads to increased porosity and surface area in materials. If this material achieves high porosity along with the naphthylamine groups, it could offer improved CO2 adsorption capacity compared to materials lacking this specific chemical composition. The combination of the unique chemical structure and enhanced porosity might result in a material that can efficiently adsorb CO2, potentially surpassing the performance of materials investigated in recent studies. Polyphosphazene-based materials are often tunable by modifying their chemical structure.

3 Characterization of synthesized HCP-A and HCP-B

3.1 Equipment

Fourier transform infrared spectroscopy (FTIR) graphs were recorded using a Thermo Nicolet Nexus 670 spectrophotometer. Elemental analysis of HCPs was determined using an energy dispersive X-ray spectroscopy (EDX). Thermogravimetry (TGA) was carried out using a Netzsch Jupiter thermal analyzer at a temperature range of 400–800°C at a heating rate of 10°C min−1. Scanning electron microscope (SEM) analysis was performed with Zeiss Ultra-55. The XRD powder (X-ray diffraction) analysis of the synthesized polymer was done with Smart Lab TM 3 kW. UV–VIS graphs were obtained from a UV–VIS spectrophotometer. For measurement of pore size, Brunauer–Emmett–Teller (BET) surface area, and pore size, CO2 adsorption/desorption isotherms on the polymers were recorded using Micromeritics ASAP 2020 M and porosity analyzer Micromeritics.

4 Results and discussion

The synthetic route for phosphazenes with a side group of 1-naphthylamine and their hyper cross-linking via Friedel crafts alkylation is shown in Figures 1 and 2. The precursor cyclic phosphazenes were obtained by reacting HCCP and 1-naphthylamine in THF at 70°C in the presence of triethylamine as a catalyst, as described in the experimental section. In another reaction, PDCP was reacted with 1-naphthylamine to produce PBNAP. Linear phosphazenes with side groups of 1-naphthylamine are displayed in Figure 3, and their hyper cross-linked reaction scheme is given in Figure 4. Linear polyphosphazenes were synthesized by replacing chloro groups of PDCP with 1-naphthylamine in THF, as reported in Section 2.

Figure 4 
               Synthesis of HCP-B (PDCP+1-naphthylamine).
Figure 4

Synthesis of HCP-B (PDCP+1-naphthylamine).

The synthesized HCP-A and HCP-B were characterized by 1H NMR and FT-IR, as discussed in the following.

The proposed structure of both HCPs is confirmed by 1H NMR, as shown in Figures 5 and 6. The peak shifting from 1H NMR of 1-naphthylamine indicates the effective grafting of 1-naphthylamine on HCCP (Figure 7).

Figure 5 
               
                  1H NMR spectra of HCCP + 1-naphthylamine (HCP-A).
Figure 5

1H NMR spectra of HCCP + 1-naphthylamine (HCP-A).

Figure 6 
               
                  1H NMR spectra of PDCP + 1-naphthylamine (HCP-B).
Figure 6

1H NMR spectra of PDCP + 1-naphthylamine (HCP-B).

Figure 7 
               IR spectrum of HCCP + 1-naphthylamine (HCP-A).
Figure 7

IR spectrum of HCCP + 1-naphthylamine (HCP-A).

4.1 IR results

Naphthylamine grafted cyclic phosphazenes showed FT-IR peaks at 1,276, 1,184(P═N), and 1,629 cm−1. Moreover, the absence of P–Cl peaks means that chlorine groups are grafted with naphthol effectively as shown in the FTIR spectra figure.

It also showed peaks at 2,880 cm−1 (–CH2– stretching vibration) and 3,267 cm−1 (–CH2– deformation vibration). The peak at 1,600 cm describes the presence of an aromatic ring. The presence of the –CH2 peak proves the effective cross-linking between polymer chains.

FT-IR spectra analysis represented polyphosphazene backbones at 1,325 and 1,020 cm−1 (–N═P– stretching band), 921 cm−1 (–N–P– stretching vibration), and 1,108 cm−1, as shown in Figure 8. In the HCP-A and HCP-B, the disappearance of chlorine showed the successful replacement of 1-naphthylamine aromatic groups and showed peaks at 2,796 cm−1 (–CH2– stretching vibration) and 3,377 cm−1 (–CH2– deformation vibration). The peak at 3,377 cm denotes the presence of the N–H group. The peak at 770 indicates the presence of C–H bending. The presence of the –CH2 peak proves the successful cross-linking between polymer chains.

Figure 8 
                  IR spectrum of PDCP+ 1-naphthylamine (HCP-B).
Figure 8

IR spectrum of PDCP+ 1-naphthylamine (HCP-B).

4.2 SEM analysis

The morphology of the HCP-A and HCP-B was investigated using an SEM, and it was found that they had abundant pores and is uniform. Because of their porous structure, these materials are very suitable for the adsorption of gases, as shown in Figures 914.

Figure 9 
                  SEM image of HCP-A at mag. 20,000.
Figure 9

SEM image of HCP-A at mag. 20,000.

Figure 10 
                  SEM image of HCP-A at mag. 40,000.
Figure 10

SEM image of HCP-A at mag. 40,000.

Figure 11 
                  SEM image of HCP-A at mag. 80,000.
Figure 11

SEM image of HCP-A at mag. 80,000.

Figure 12 
                  SEM image of HCP-B at mag. 20,000.
Figure 12

SEM image of HCP-B at mag. 20,000.

Figure 13 
                  SEM image of HCP-B at mag. 40,000.
Figure 13

SEM image of HCP-B at mag. 40,000.

Figure 14 
                  SEM image of HCP-B at mag. 50,000.
Figure 14

SEM image of HCP-B at mag. 50,000.

XRD graphs of HCP-A and HCP-B are shown in Figures 15 and 16, respectively. It can be observed from the figures that there is no sharp peak at 2θ, and it has some noisy pattern, which suggests that both polymers are amorphous in nature.

Figure 15 
                  XRD graph of HCP-A.
Figure 15

XRD graph of HCP-A.

Figure 16 
                  XRD graph of HCP-B.
Figure 16

XRD graph of HCP-B.

4.3 Percentage composition

The percentage composition of HCP-A and HCP-B shows that nitrogen and phosphorous content are present in abundance in HCP-A compared to HCP-B, which has a low concentration of nitrogen and phosphorous. This is due to the cyclic nature of HCP-A (Table 1).

Table 1

Elemental percentage composition of HCP-A and HCP-B

Sr. No Elements % Compositions
HCP-A HCP-B
1. Weight 2.1740 1.979
2. Nitrogen 10.73 1.01
3. Carbon 76.99 62.00
4. Hydrogen 7.498 5.19
5. Phosphorus 0.5 0.03

4.4 UV results

HCP-A shows lambda max at 352 nm with an absorbance of 1.394, and HCP-B shows lambda max at 291 nm with an absorbance of 1.49 (Figures 17 and 18).

Figure 17 
                  UV–Vis graph of HCP-A.
Figure 17

UV–Vis graph of HCP-A.

Figure 18 
                  UV–Vis graph of HCP-B.
Figure 18

UV–Vis graph of HCP-B.

4.5 Thermogravimetric analysis

TGA studies in the CO2 atmosphere showed that HCP-A and HCP-B are thermally stable under 420°C (HCP-A) and stable even higher than 800°C (HCP-B). It was observed that the first 5% weight loss was due to the volatilization of solvent adsorbed in the HCP surface, as shown in Figure 19. HCP-B degraded rapidly from 200 to 600°C, later becoming constant, and weight loss was not more than 60% even at 800°C while HCP-A degraded after 200°C very fast, and at 600°C it became constant and weight loss was 40. It was found that HCP-B is thermally more stable than HCP-A due to long-chain nitrogen and phosphorus backbone, so we conclude that HCP-B was not easily degraded.

Figure 19 
                  TGA of HCP-A and HCP-B.
Figure 19

TGA of HCP-A and HCP-B.

4.6 Porosity

The porosity of the HCP-A and HCP-B was investigated by adsorption analysis using CO2 gas as the adsorbate molecule, and HCPs act as the adsorbent. Before adsorption, the materials were de-gassed at 120°C for 8 h under a nitrogen atmosphere. The porosity and surface area of HCP-A and HCP-B were studied by CO2 adsorption–desorption measurements at 77 K. The results are shown in Figures 20 and 21. HCP-A and HCP-B porous networks were investigated with a BET surface area of 170.89 m2 g−1 and 492.03 m2 g−1 respectively.

Figure 20 
                  Brunauer–Emmett–Teller plot and pore size distribution of HCP-A.
Figure 20

Brunauer–Emmett–Teller plot and pore size distribution of HCP-A.

Figure 21 
                  Brunauer–Emmett–Teller plot and pore size distribution of HCP-B.
Figure 21

Brunauer–Emmett–Teller plot and pore size distribution of HCP-B.

4.7 CO2 uptake capacity

Due to the increase in the level of CO2, scientists are finding ways to CO2 capturing. HCPs are very useful in capturing CO2 due to their characteristics, including low density, large surface area, thermal stability, smaller pore size, and easy functionalization [39]. Now, HCPs are widely studied as adsorbents to reduce CO2 concentration in the environment. For example, CO2 capturing capacity was tested in different types of MOP networks. This HCP was prepared by cross-linking of tetraphenylmethane by using FDA and catalyst FeCl3. It was found and reported that CO2 adsorption was 2.95 mmol/g at 273 K temperature and 1 bar pressure. Researchers have evaluated CO2 adsorption and its conversion into organic compounds. For example, the synthesis of imidazolium salt-modified porous HCPs shows CO2 adsorption up to 14.5 wt% at 273 K and 1 bar pressure. Such functionalized materials showed high activity to change it into cyclic carbonates. This is because of the synergistic effect of the salt used and the micro-porosity of the polymers [40].

The synthesized HCP has a high surface area, which enables it to be used for CO2 adsorption. HCP-A showed a lower level of CO2 adsorption ability of 5.2 mmol g−1 at 273 K and 4.21 mmol g−1 at 298 K as compared to HCP-B, exhibited a higher CO2 adsorption ability of 7.20 mmol g−1 at 273 K and 4.30 mmol g−1 at 298 K, as shown in Figure 22 which is due to less surface area of HCP-A as compared to HCP-B.

Figure 22 
                  CO2 adsorption–desorption isotherm of HCP-A and HCP-B.
Figure 22

CO2 adsorption–desorption isotherm of HCP-A and HCP-B.

4.8 Isosteric heat of adsorption of CO2

For further understanding of the relationship between HCP-A and HCP-B toward CO2 adsorption, the isosteric heat of adsorption (Q st) was determined with the help of CO2 isotherms measured at 273 and 298 K. Two isotherms were obtained at two different temperatures with CO2 sorption on HCP-A and HCP-B. Q st was determined by the following formula. It shows the advantage of capturing the effect of surface coverage upon enthalpy of adsorption

Q st = R [ ( T 2 × T 1 ) / ( T 2 T 1 ) ] / In ( P 2 / P 1 ) .

From the graph, it was found that at a lower temperature, the kinetic energy of CO2 molecules seized and indicated higher adsorption ability of HCP-A and HCP-B, while upon increasing the temperature, the CO2 gas molecule released at a higher rate and showed less adsorption (Table 2).

Table 2

Summary of CO2 uptake and Q st by HCP-A and HCP-B

Polymer CO2 uptake at 273 K (%) CO2 uptake at 298 K (%) Q st for CO2 uptake (kJ/mol)
HCP-A 5.2 7.20 30.2–26.5
HCP-B 4.21 4.30 28.3–27.3

Figure 23 shows that the heat of adsorption of HCP-B is greater than HCP-A, and it decreases as the quantity of CO2 adsorbed increases. HCP-A shows less heat of adsorption as compared to HCP-B due to its structure.

Figure 23 
                  CO2 adsorption isotherm at STP of HCP-A and HCP-B.
Figure 23

CO2 adsorption isotherm at STP of HCP-A and HCP-B.

5 Conclusion

The presence of clean air is essential for sustaining life. However, as a result of industrialization, population growth, and the usage of fossil fuels, the levels of hazardous chemicals and greenhouse gases are steadily rising. Developing cost-effective and environmentally friendly methods to purify air has become a significant challenge for scientists. We have synthesized two porous hybrid polymers using phosphazenes as a starting material. These polymers are rich in phosphorus and nitrogen. The synthesis involved replacing the chlorine atoms of HCCP with 1-naphthylamine, followed by cross-linking through the Friedel–Crafts alkylation. PDCP, a different polymer, was synthesized and then underwent chlorination replacement with 1-naphthylamine. It was then cross-linked, as described earlier. The polymers HCP-A and HCP-B exhibited a significant presence of micro-pores, a favorable surface area, and exceptional thermal stability. The BET surface area of the HCP-A porous network is 170.89 m2 g−1, while the HCP-B porous network has a BET surface area of 492.03 m2 g−1. Additionally, it was discovered that the phosphorus and nitrogen levels in HCP-A and HCP-B promoted the absorption of CO2. This study presents a new approach for the systematic production of highly effective nitrogen- and phosphorus-based HCPs with the ability to adsorb gases in their micropores.

6 Future perspective

Hyper cross-linked polyphosphazenes with naphthylamine group materials have great selectivity and capacity for CO2 capture, along with good stability and regeneration capabilities, and they have the potential for promising future possibilities. If they demonstrate efficacy and cost-effectiveness, they could be applied in various practical contexts.

It has the potential to be utilized in businesses such as power plants, where there is a significant amount of CO2 emissions, to capture CO2 prior to its release into the environment, thereby mitigating greenhouse gas emissions. This technology could be utilized in gas purification operations to effectively eliminate CO2 from natural gas or biogas streams. Possible applications could encompass environmental remediation endeavors, such as the removal of CO2 from enclosed areas or the capture of emissions from vehicles. This area of study shows potential in aiding worldwide efforts to address climate change by absorbing and neutralizing CO2 emissions. However, additional testing, optimization, and economic evaluations are required to ensure its successful integration in everyday situations.

Acknowledgments

This work was supported by the National Research Foundation of Korea (NRF) grant funded by the Korea government (MSIT) (RS-2024-00357072) and Researchers Supporting Project number (RSPD2024R765), King Saud University, Riyadh, Saudi Arabia.

  1. Funding information: This work was supported by the National Research Foundation of Korea (NRF) grant funded by the Korea government (MSIT) (RS-2024-00357072) and Researchers Supporting Project number (RSPD2024R765), King Saud University, Riyadh, Saudi Arabia. M. La was supported by the National Research Foundation of Korea (NRF) grant funded by the Korea government (MSIT) (No. 2022R1C1C1003091).

  2. Author contributions: All authors have accepted responsibility for the entire content of this manuscript and approved its submission.

  3. Conflict of interest: The authors state no conflict of interest.

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Received: 2023-11-09
Revised: 2023-12-29
Accepted: 2024-01-02
Published Online: 2024-06-21

© 2024 the author(s), published by De Gruyter

This work is licensed under the Creative Commons Attribution 4.0 International License.

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