Open Access Article
Qihaoyue
Wang‡
,
Lin
Lin‡
,
Li
Jiang
,
Zihao
Wang
,
Yina
Zhang
,
Qiance
Han
,
Xin
Huang
,
Changyan
Zhu
,
Jiangtao
Jia
*,
Zheng
Bian
* and
Guangshan
Zhu
*
Key Laboratory of Polyoxometalate and Reticular Material Chemistry of Ministry of Education, Faculty of Chemistry, Northeast Normal University, Changchun, Jilin 130024, China. E-mail: jiangtaojia@nenu.edu.cn; bianz070@nenu.edu.cn; zhugs@nenu.edu.cn
First published on 1st July 2025
Herein, we report the development of a post-synthetic modification approach to introduce a high loading of formyl groups onto porous aromatic framework (PAF)-5 via Friedel–Crafts alkylation followed by hydrolysis. Rigorous characterization by NMR, X-ray photoelectron spectroscopy, and Fourier-transform infrared spectroscopy authenticated the successful integration of aldehyde moieties into PAF-5, affording PAF-5-CHO. Subsequent functionalization of PAF-5-CHO with various amines produced three amine-functionalized PAF derivatives. Notably, PAF-5-C
N-EDA exhibited a 78% enhancement in carbon dioxide (CO2) adsorption capacity, reaching 3.78 mmol g−1 at 1 bar and 298 K relative to PAF-5-CHO. Breakthrough experiments demonstrated that PAF-5-C
N-EDA could effectively separate CO2 from simulated flue gas (CO2/N2 = 15
:
85, v/v; 10 mL min−1). In situ infrared spectroscopy, density functional theory calculations and temperature-programmed desorption studies provided insights into the CO2 adsorption mechanism.
There are five principal methods for capturing CO2: membrane separation, solvent-based absorption, physical adsorption, cryogenic separation, and chemical looping.4 Among these, aqueous amine solutions, which capture CO2via the formation of carbamates or bicarbonates, remain the most mature and widely applied technology. However, aqueous amine systems suffer from significant drawbacks, including volatility, oxidative degradation, equipment corrosion, and high operational costs.5 Due to these limitations, several new CCS methods have emerged in recent years, among which solid porous materials, such as activated carbons, metal–organic frameworks (MOFs), porous organic polymers (POPs), silica, and zeolites, have received considerable attention and extensive research.6–11 These materials offer advantages like high adsorption efficiency, low energy consumption, stability, and ease of regeneration.
Post-synthetic modification (PSM) is a vital approach for developing and enhancing solid materials such as MOFs and POPs, offering extensive functionality and broad applicability.12–19 Incorporating CO2-philic functional groups into porous materials by PSM has been proven to enhance strong interactions between CO2 and materials, significantly improving their selectivity for CO2 capture.20–24 Porous aromatic frameworks (PAFs), a subset of POPs, possess high specific surface areas and porosities, which significantly enhance gas contact efficiency. PAFs are typically constructed through C–C covalent bonds, and their robust skeletons confer high chemical stability, enabling them to withstand harsh conditions during the PSM process. In previous studies, PSM has been used to introduce functional groups such as –SH, –NH2, –SO3H, and –Cl into PAF frameworks, enabling their applications in areas such as seawater desalination, gas adsorption, and catalysis.25–36 In addition, PAFs are ideal candidates for the incorporation of CO2-philic functional groups, which can strongly interact with CO2 and thus facilitate efficient capture.
In this study, we propose a new PSM strategy to enhance the CO2 capture efficiency of PAFs. This method allows for the simple and efficient introduction of aldehyde groups into the PAF framework by way of the Friedel–Crafts reaction, resulting in the synthesis of PAF-5-CHO. Notably, direct PSM of –CHO groups in the frameworks has not yet been reported. The aldehyde group has the potential to be transformed into different functional groups.37,38 Accordingly, PAF-5-CHO was further functionalized with amino groups via Schiff base reactions with organic amines aiming to enhance CO2 capture performance. The resulting series of amino-functionalized PAFs exhibit excellent CO2 capture and separation properties.
O bond of aldehyde groups,23 while the peak at 783 cm−1 was attributed to the unhydrolyzed C–Cl bond.27 The formation mechanism of aldehyde groups in PAF-5-CHO by way of Friedel–Crafts alkylation and acidic hydrolysis is illustrated in Fig. 1e. Notably, the method to introduce –CHCl2 groups by Friedel–Crafts alkylation is limited to the rigid organic framework. In the rigid aromatic porous material, these –CHCl2 groups can't further react with other aromatic units, making them completely stay on the framework.
Additionally, the high-resolution C 1s XPS spectrum of PAF-5 (Fig. S2†) shows only a single peak corresponding to C–C bonds. In contrast, the C 1s spectrum of PAF-5-CHO displays new peaks at 286.5 eV and 288.7 eV, corresponding to C–Cl and C
O bonds, respectively.42 Elemental oxygen analysis of PAF-5-CHO (Table S1†) reveals an oxygen content of 7.475 wt%, indicating the introduction of approximately 1.5 aldehyde groups per structural unit of PAF-5. However, thermogravimetric analysis (TGA) results (Fig. S3a†) show a weak thermal stability for PAF-5-CHO compared to PAF-5 due to the lower pyrolysis temperature of –CHO groups than aromatic groups. Furthermore, the scanning electron microscope (SEM) images (Fig. S4a–c†) exhibit no marked changes after the modification process. Powder X-ray diffraction (PXRD) patterns (Fig. S5†) indicate that PAF-5-CHO remains an amorphous material.
N-EDA, PAF-5-C
N-DETA, and PAF-5-C
N-TETA (Fig. 2b), the emergence of –NH2 vibration at 3300 cm−1 and –C
N vibration at 1640 cm−1 confirms the successful occurrence of the Schiff base reaction.23 In the XPS total spectrum (Fig. 2c), the presence of the N element can be clearly evident. Additionally, in the high-resolution N 1s XPS spectra of PAF-5-C
N-EDA, PAF-5-C
N-DETA, and PAF-5-C
N-TETA (Fig. S6†), the peaks at 398.6 eV, 398.3 eV, and 398.2 eV are assigned to C
N bonds, while the peaks at 399.4 eV, 399.1 eV, and 399 eV correspond to –NH2 and –NH– species.43–45 Elemental analysis (Table S2†) further supports the formation of imine bonds, showing a significant increase in nitrogen content for the three amine-functionalized materials compared to PAF-5-CHO. Among them, PAF-5-C
N-TETA exhibits the highest nitrogen content at 10.04 wt%, equivalent to approximately 0.8 -NH2 groups per triphenyl benzene unit of PAF-5. Based on these data, it can be inferred that around 50% of the aldehyde groups participate in the reaction. Moreover, TGA analysis (Fig. S3b†) demonstrates that the amine-functionalized PAF-5-CHO materials retain stability in air up to 235 °C. The weight loss observed between 235 °C and 520 °C is attributed to the decomposition of the amine chains.20 SEM images (Fig. S4d–f†) reveal no significant morphological changes in the materials after amine modification.
N-EDA, PAF-5-C
N-DETA, and PAF-5-C
N-TETA at 77 K are shown in Fig. 3a. Their corresponding Brunauer–Emmett–Teller (BET) surface areas are 1660, 1510, 1423, 1224, and 1101 m2 g−1, respectively. The reduction in the BET surface area for PAF-5-CHO is likely due to the aldehyde groups occupying the pore channels, as evidenced by the decrease in pore width from 1.75 nm to 1.03 nm (Fig. S7†). PAF-5-C
N-EDA, PAF-5-C
N-DETA, and PAF-5-C
N-TETA exhibit further reductions in both BET surface area and pore volume relative to PAF-5-CHO. When the transformation of aldehyde groups into long-chains happens, the materials become heavier and the larger amine molecules occupy more pore space. Fig. 3b and S8† illustrate the CO2 adsorption isotherms of PAF-5-CHO and the three amine-functionalized PAF-5 materials at 298 K and 273 K. Across the entire experimental pressure range (0–100 kPa), the CO2 adsorption capacity of PAF-5-C
N-EDA, PAF-5-C
N-DETA, and PAF-5-C
N-TETA shows a remarkable improvement compared to PAF-5-CHO. This demonstrates that organic amine modification significantly enhances CO2 adsorption performance. Among the three materials, PAF-5-C
N-EDA shows the greatest improvement in CO2 adsorption capacity, primarily attributed to its high specific surface area and the high loading of amine. Specifically, at 298 K, the CO2 adsorption capacity of PAF-5-C
N-EDA is 3.78 mmol g−1, which represents a 78% increase compared to PAF-5-CHO, and the adsorption capacity remains nearly unchanged after six cycles (Fig. S9†).
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| Fig. 3 (a) N2 uptake at 77 K; (b) CO2 uptake of PAF-5-CHO and its derivations at 298 K; (c) CO2 −Qst of PAF-5-CHO and its derivation; (d) comparison of CO2 uptake with other amine-functionalized POPs at 15 kPa and 100 kPa.20,46–57 | ||
Flue gas emitted from coal-fired power plants contains approximately 15% CO2 at 100 kPa, thus the CO2 adsorption capacity at 15 kPa is highly relevant for practical applications. At 298 K and 15 kPa, among the three amine-functionalized materials, PAF-5-C
N-TETA exhibits the highest CO2 adsorption capacity (Fig. S10†). Despite having the lowest BET surface area, PAF-5-C
N-TETA shows the highest nitrogen content—10.004% (Table S2†). This indicates that at low pressure, CO2 adsorption is more strongly influenced by the amine group content rather than the BET surface area. Specifically, at 298 K and 15 kPa, the CO2 adsorption capacity of PAF-5-CHO is 0.41 mmol g−1, while that of PAF-5-C
N-TETA reaches 1.18 mmol g−1, representing a twofold increase compared to PAF-5-CHO.
Furthermore, the isosteric enthalpy of adsorption (Qst) plot (Fig. 3c) determined from adsorption isotherm calculations at 273 K and 298 K shows that all three materials obtained after organic amine modification are significantly improved compared to PAF-5-CHO. The −Qst of PAF-5-CHO is 25 kJ mol−1, whereas PAF-5-C
N-TETA, PAF-5-C
N-DETA, and PAF-5-C
N-EDA exhibit higher −Qst values of 34, 33, and 32 kJ mol−1, respectively. Moreover, the CO2 desorption isothermal curves of these three materials do not exhibit significant hysteresis loops, indicating their excellent cycling potential. Compared to other amine-functionalized POPs (Fig. 3d), the three materials presented in this study exhibit higher adsorption capacities at both 15 kPa and 100 kPa. Thus, these materials demonstrate considerable promise for utilization in CO2 capture and recovery applications.
N-EDA
N-EDA for subsequent CO2/N2 separation experiments. Using the CO2 and N2 adsorption isotherms of PAF-5-C
N-EDA at 298 K (Fig. 4a), the CO2/N2 selectivity was calculated using the Ideal Adsorbed Solution Theory (IAST) method. Fig. 4b shows that the CO2/N2 selectivity of PAF-5-C
N-EDA is approximately 37. To evaluate its actual separation performance, breakthrough experiments were conducted using 0.075 g of PAF-5-C
N-EDA powder. At 298 K and 1 bar, a CO2/N2 (15
:
85, v/v) gas mixture was passed through a tightly packed fixed-bed column containing PAF-5-C
N-EDA at a flow rate of 10 mL min−1. As shown in Fig. 4c, N2 breakthrough occurred almost immediately, while CO2 breakthrough was delayed for a retention time (15 min g−1), demonstrating excellent CO2 separation performance. The CO2 capture capacity calculated from a single breakthrough experiment was 1.00 mmol g−1, consistent with the results from the CO2 adsorption isotherm. After eleven consecutive breakthrough cycles (Fig. S11 and S12†), the material retained good separation performance, with an average CO2 adsorption capacity of 1.75 mmol g−1 during the breakthrough process.
N-EDA framework and CO2 molecules. Five potential CO2 adsorption configurations were constructed and optimized (Fig. S13†). The calculated adsorption energies reveal that the interaction between the amine group and the C atom of CO2 represents the dominant contribution, exhibiting the lowest adsorption energy (−0.31 eV). This suggests that the amine groups serve as the most favorable active sites for CO2 adsorption. In this configuration, the N–C distance measures 2.76 Å, which is shorter than their sum of van der Waals radius. Additionally, the O–C–O angle of the adsorbed *CO2 deviates slightly from linearity, changing from 180° to 175.0°. Charge transfer analysis indicates electron donation from PAF-5-C
N-EDA to the adsorbed *CO2, with a Bader charge of 0.14|e| localized on *CO2. These results demonstrate that the adsorbed *CO2 undergoes activation, consistent with the observed negative adsorption energy. To further assess the diffusion rate of CO2 molecules on the PAF-5-C
N-EDA model, we examined the diffusion pathway and the corresponding energy barrier of a single CO2 molecule moving between two adjacent amine active sites (Fig. S14†). The computed diffusion barrier is remarkably low (0.09 eV), suggesting that CO2 molecules can diffuse rapidly through the porous structure of the material.
We conducted in situ IR spectroscopy to monitor the adsorption process of CO2 on PAF-5-C
N-EDA. During the experiment, CO2 gas flowed through the PAF-5-C
N-EDA adsorbent. The absorption spectra shown in Fig. S15† were obtained by collecting the PAF-5-C
N-EDA absorption spectra as a background, and the band produced by absorbed CO2 at 2360 cm−1 can be observed.58 In the IR spectra of PAF-5-C
N-EDA with adsorbed CO2 (Fig. 5b), the following features were identified: (i) the O
C
O− band of carbamate NHCOO− at 1532 cm−1 and (ii) the +N–H band of NH3+ at 1656 cm−1. The adsorption mechanism inferred from the in situ IR analysis is illustrated in Fig. 5a, and the process occurs in two stages. To further confirm the adsorption mechanism, temperature-programmed desorption (TPD) of the post-breakthrough sample was performed (Fig. 5c). The first desorption peak corresponds to weakly adsorbed CO2 on the adsorbent and the column walls, while the second peak, appearing at temperatures above 100 °C, corresponds to the intermediate species described as Stage I in the mechanism diagram. A third peak represents the desorption of CO2 species associated with Stage II of the mechanism temperatures above 100 °C, corresponding to the intermediate species described as Stage I in the mechanism diagram. A third peak represents the desorption of CO2 species associated with Stage II of the mechanism.
N-EDA exhibits excellent performance in capturing post-combustion CO2. Through the investigation of the CO2 adsorption mechanism, it was found that there are two distinct adsorption sites involved in the process. This study highlights the potential of this class of materials in post-combustion CO2 capture technology.
N-EDA as an example: PAF-5-C
N-EDA (100 mg) and ethylenediamine (EDA, 10 mL) were added to a sealed flask. The mixture was kept at 80 °C for 3 days. The solid was filtered, washed with water and methanol, and then dried in vacuo to produce PAF-5-C
N-EDA as a brown powder in quantitative yield.
N-EDA was loaded onto a stainless-steel column (1 mL volume, 0.45 cm inner diameter). A CO2/N2 (15:
85, v/v) gas mixture was allowed to flow into the column. A mass spectrometer (Master 400) was used to monitor the gas flow from the column.
Footnotes |
| † Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d5sc00355e |
| ‡ Q. Wang and L. Lin contributed equally to this paper. |
| This journal is © The Royal Society of Chemistry 2025 |