Open Access Article
Muhamad Salam Ahmad
* and
Farouq Emam Hawaiz
Department of Chemistry, College of Education, Salahaddin University-Erbil, Kurdistan, Iraq. E-mail: muhamedsalam15@gmail.com
First published on 11th January 2024
Macrocycles play a pivotal and indispensable role within the realms of both medicine and industry. In the course of our research endeavors, we have successfully synthesized five distinct macrocyclic chalcone entities, each showcasing remarkable biological and anti-oxidative properties. Furthermore, these compounds exhibit exceptional promise as potent agents for the removal of dyes in wastewater treatment processes. The synthesis of these key constituents was achieved through the judicious application of the Robinson ether synthesis and Claisen–Schmidt condensation reactions. The structures of compounds 1a–f and 2a–e were characterized by using analytical techniques such as FTIR, 1H NMR, 13C NMR, and DEPT 13C NMR spectroscopy. These macrocycles also underwent in vitro assessments to measure their antibacterial activity using the agar well diffusion method. The results revealed that the macrocyclics were more sensitive to Gram-positive than Gram-negative bacteria. For example, compound 2d exhibited an inhibition zone of 20 mm at 150 ppm. The antioxidant activity as determined via the DPPH method established that all tested compounds showed moderate radical-scavenging ability. Specifically, compound 2e (at 1000 ppm) exhibited antioxidant activity of 79% inhibition of radicals, in comparison to 90% for the standard ascorbic acid. The latter was demonstrated by using methylene blue as an adsorbate under simulated wastewater conditions. Outstandingly, the most effective compounds were 2d and 2c, which achieved removal rates of 96.54% and 92.37%, respectively, for methylene blue dye.
Many macromolecules are composed of bis-aldehydes and bis-ketones. Chalcone moiety macrocycles10 and macrocycles with other functional groups11 have been previously prepared and tested in the aforementioned fields, yielding acceptable results.12 Their potential to address existing challenges in the above-mentioned areas is evident from the magnitude of their impact. To address human health concerns and mitigate the influence of harmful microorganisms, researchers are actively promoting the development and synthesis of novel biologically active compounds. This has become a crucial aspect of scientific research requirements. The exploration of new compounds with beneficial physiological effects, particularly through extensive studies on macrocycles, has led to the emergence of various methods for their preparation.13 Chalcone moiety macrocycles are considered useful organic compounds due to their wide range of applications in the fields of health,14 as anti-inflammatory, anti-bacterial, and anti-viral agents. The most important uses in the environmental field include contaminant removal from wastewater,15 and in industry, they are used as catalysts in chemical reactions.16
Water resource contamination is a highly contested global issue due to its severe and often lasting impact on living organisms.17 Among the various pollutants, the presence of dyes in water is particularly concerning because they can alter the natural appearance of water even at very low concentrations. There is a great deal of environmental pollution of dyes due to the vast array of existing dyes and an annual production reaching approximately 1.6 million tons. Methylene blue (MB) is the most commonly used dye and was first synthesized in 1876 by Heinrich Caro of Badische Anilin and Soda-Fabrik (BASF). Initially created as an aniline-based synthetic dye for coloring cotton in the textile industry, it was soon recognized for its utility in staining and deactivating microbial species.18
Based on this, we created a series of macrocyclic compounds containing two chalcone groups and four ether groups via adducting both Robinson ether synthesis reactions to prepare bis-aldehyde and bis-ketone intermediate linkages.19 The Claisen–Schmidt condensation reaction was used to condense linkages and obtain five macrocycle chalcone moieties as the final products.20 We proceeded to perform a series of tests aimed at assessing their biological activities, antioxidative properties, and their efficacy in purifying water-containing pollutants. To elucidate the chemical structures of the intermediates and final products, a comprehensive array of analytical techniques, including Fourier transform infrared (FTIR), proton (1H) NMR, carbon-13 (13C) NMR, and distortionless enhancement by polarization transfer (DEPT) 13C NMR spectroscopy, was employed.
O), 1597 (C
C). 1H-NMR (δ, ppm): 1.59 (p, 4H, H10,10′), 1.09 (p, 4H, H9,9′), 4.09 (t, 4H, H8,8′), 6.98 (combinate dd, 2H, H2,2′), 7.00 (combinate td, 2H, H4,4′), 7.53 (td, 2H, H3,3′), 7.81 (dd, 2H, H5,5′), 10.50 (s, 2H, H7,7′), 13C-NMR (δ, ppm): 25.86: C10,10′, 29.06: C9,9′, 68.26: C8,8′, 112.48: C2,2′, 120.58: C4,4′, 124.87: C6,6′, 128.29: C5,5′, 136.00: C3,3′, 161.46: C1,1′, 189.84: C7,7′. 13C-DEPT-135 (δ, ppm): 25.86: C10,10′, 29.06: C9,9′, 68.26: C8,8′, 112.48: C2,2′, 120.58: C4,4′, 128.29: C5,5′, 136.00: C3,3′, 189.84: C7,7′.
O), 1602.85 (C
C). 1H-NMR (δ, ppm): 4.72 (q, 4H, H8,8′), 6.16 (p, 2H, H9,9′), 6.99 (dd 2H, H2,2′), 7.05 (td, 2H, H4,4′), 7.55 (td, 2H, H3,3′), 7.85 (dd, 2H, H5,5′), 10.50 (s, 2H, H7,7′), 13C-NMR (δ, ppm): 67.98: C8,8′, 112.76: C2,2′, 121.10: C4,4′, 125.10: C6,6′, 127.86: C9,9′, 128.71: C5,5′, 135.92: C3,3′, 160.67: C1,1′, 189.64: C7,7′. 13C-DEPT-135 (δ, ppm): 67.98: C8,8′, 112.76: C2,2′, 121.10: C4,4′, 127.86: C9,9′, 128.71: C5,5′, 135.92: C3,3′, 189.64: C7,7′.
O), 1600.92 (C
C). 1H-NMR (δ, ppm): 2.09 (p, 4H, H9,9′), 4.18 (t, 4H, H8,8′), 6.98 (dd, 2H, H2,2′), 7.02 (td, 2H, H4,4′), 7.53 (td, 2H, H3,3′), 7.80 (dd, 2H, H5,5′), 10.49 (s, 2H, H7,7′). 13C-NMR (δ, ppm): 25.93: C9,9′, 67.85: C8,8′, 112.39: C2,2′, 120.77: C4,4′, 124.84: C6,6′, 128.51: C5,5′, 136.03: C3,3′, 161.17: C1,1′, 189.59: C7,7′. 13C-DEPT-135 (δ, ppm): 25.93: C9,9′, 67.85: C8,8′, 112.38: C2,2′, 120.77: C4,4′, 128.50: C5,5′, 136.04: C3,3′, 189.60: C7,7′.
O), 1612.49 (C
C). 1H-NMR (δ, ppm): 1.58 (p, 4H, H11,11′), 1.89 (p, 4H, H10,10′), 2.62 (s, 6H, H8,8′), 4.04 (t, 4H, H9,9′), 6.89 (d, 2H, H2,2′), 7.13 (dd, 2H, H3,3′), 7.45 (d, 2H, H5,5′). 13C-NMR (δ, ppm): 25.99: C11,11′, 29.17: C10,10′, 31.95: C8,8′, 68.92: C9,9′, 113.55: C5, 113.63: C5′, 116.41: C2, 116.65: C2′, 119.95: C3, 120.18: C3′, 128.93: C6, 128.98: C6′, 154.63: C4, 154.65: C4′, 155.43: C1, 157.82: C1′, 198.39: C7, 198.40: C7′. 13C-DEPT-135 (δ, ppm): 25.99: C11,11′, 29.17: C10,10′, 31.96: C8,8′, 68.92: C9,9′, 113.55: C5, 113.62: C5′, 116.41: C2, 116.65: C2′, 119.96: C3, 120.18: C3′.
O), 1593.20 (C
C). 1H-NMR (δ, ppm): 1.59 (p, 4H, H11,11′), 1.90 (p, 4H, H10,10′), 2.62 (s, 6H, H8,8′), 4.07 (t, 4H, H9,9′), 6.94 (combine dd, 2H, H2,2′), 6.97 (combine td, 2H, H4,4′), 7.43 (td, 2H, H3,3′), 7.73 (dd, 2H, H5,5′). 13C-NMR (δ, ppm): 26.02: C11,11′, 29.17: C10,10′, 32.08: C8,8′, 68.24: C9,9′, 112.24: C2,2′, 120.47: C4,4′, 128.27: C6,6′, 130.40: C5,5′, 133.70: C3,3′, 158.39: C1,1′, 199.93: C7,7′. 13C-DEPT-135 (δ, ppm): 26.02: C11,11′, 29.17: C10,10′, 32.08: C8,8′, 68.24: C9,9′, 112.24: C2,2′, 120.47: C4,4′, 130.41: C5,5′, 133.70: C3,3′.
O), 1610.56 (C
C).
O), 1587.42 (C
C). 1H-NMR (δ, ppm): 1.85 (p, 4H, H18,18′), 3.95 (p, 4H, H17,17′), 4.21 (t, 4H, H16,16′), 6.69 (dd, 2H, H2,2′), 6.76 (td, 2H, H4,4′), 6.91 (d, 2H, H14,14′), 7.04 (td, 2H, H3,3′), 7.13 (dd, 2H, H13,13′), 7.36 (d, 2H, H11,11′), 7.40 (dd, 2H, H5,5′), 7.62 (d, 2H, H8,8′), 7.71 (d, 2H, H7,7′). 13C-NMR (δ, ppm): 26.20: C18,18′, 67.94: C17,17′, 68.56: C16,16′, 111.93: C11,11′, 115.39: C2, 115.47: C2′, 115.98: C14, 116.23: C14′, 117.94: C4, 118.17: C4′, 121.07: C13,13′, 123.33: C10,10′, 127.92: C8,8′, 130.51: C3,3′, 131.46: C6,6′, 132.07: C5,5′, 141.65: C7,7′, 152.41: C15,15′, 155.96: C1,1′, 158.03: C12,12′, 193.95: C9,9′. 13C-DEPT-135 (δ, ppm): 26.20: C18,18′, 67.93: C17,17′, 68.55: C16,16′, 111.92: C11,11′, 115.39: C2, 115.46: C2′, 115.99: C14, 116.23: C14′, 117.95: C4, 118.18: C4′, 121.07: C13,13′, 127.91: C8,8′, 130.52: C3,3′, 132.08: C5,5′, 141.65: C7,7′.
O), 1595.13 (C
C). 1H-NMR (δ, ppm): 1.49 (p, 4H, H19,19′), 2.73 (p, 4H, H18,18′), 3.96 (t, 4H, H17,17′), 4.29 (t, 4H, H16,16′), 6.75 (td, 2H, H4,4′), 6.83 (dd, 2H, H2,2′), 6.87 (d, 2H, H14,14′), 6.94 (td, 2H, H3,3′), 7.24 (dd, 2H, H13,13′), 7.29 (d, 2H, H11,11′), 7.45 (dd, 2H, H5,5′), 7.53 (d, 2H, H8,8′), 7.82 (d, 2H, H7,7′). 13C-NMR (δ, ppm): 26.23: C19,19′, 28.84: C18,18′, 68.33: C17,17′, 68.70: C16,16′, 112.03: C11,11′, 115.21: C2, 115.29: C2′, 116.71: C14, 116.95: C14′, 118.60: C4, 118.83: C4′, 120.56: C13,13′, 123.69: C10,10′, 127.51: C8,8′, 130.20: C3,3′, 131.18: C6,6′, 131.71: C5,5′, 140.72: C7,7′, 153.13: C15,15′, 156.06: C1,1′, 158.25: C12,12′, 191.77: C9,9′. 13C-DEPT-135 (δ, ppm): 26.24: C19,19′, 28.84: C18,18′, 68.33: C17,17′, 68.69: C16,16′, 112.02: C11,11′, 115.20: C2, 115.27: C2′, 116.72: C14, 116.96: C14′, 118.61: C4, 118.84: C4′, 120.56: C13,13′, 127.50: C8,8′, 130.20: C3,3′, 131.71: C5,5′, 140.72: C7,7′.
O), 1598.99 (C
C). 1H-NMR (δ, ppm): 1.21 (p, 4H, H20,20′), 1.47 (p, 4H, H19,19′), 3.94 (t, 4H, H18,18′), 4.62 (d, 4H, H16,16′), 5.97 (t, 2H, H17,17′), 6.89 (dd, 4H, H2,2′,14,14′), 6.95 (td, 2H, H4,4′), 7.01 (td, 2H, H3,3′), 7.31 (td, 2H, H12,12′), 7.40 (m, 4H, H8,8′,13,13′), 7.55 (dd, 4H, H5,5′,11,11′), 7.79 (d, 2H, H7,7′). 13C-NMR (δ, ppm): 25.68: C18,18′, 28.73: C17,17′, 68.04: C16,16′, 68.35: C19,19′, 112.46: C2,2′, 112.74: C14,14′, 120.59: C12,12′, 121.16: C4,4′, 124.47: C6,6′, 127.94: C8,8′, 128.64: C11,11′, 129.65: C3,3′, 130.02: C10,10′, 130.06: C20,20′, 131.35: C13,13′, 132.38: C5,5′, 138.90: C7,7′, 157.36: C15,15′, 157.46: C1,1′, 194.73: C9,9′. 13C-DEPT-135 (δ, ppm): 25.68: C18,18′, 28.73: C17,17′, 68.04: C16,16′, 68.35: C19,19′, 112.46: C2,2′, 112.74: C14,14′, 120.59: C12,12′, 121.16: C4,4′, 127.94: C8,8′, 128.64: C11,11′,129.66: C3,3′, 130.06: C20,20′, 131.35: C13,13′, 132.39: C5,5′, 138.90: C7,7′.
O), 1587.42 (C
C). 1H-NMR (δ, ppm): 1.17 (p, 4H, H21,21′), 1.39 (p, 4H, H18,18′), 1.52 (p, 4H, H20,20′), 1.80 (p, 4H, H17,17′), 3.72 (t, 4H, H19,19′), 4.04 (t, 4H, H16,16′), 6.75 (dd, 2H, H2,2′), 6.87 (d, 2H, H14,14′), 6.91 (d, 2H, H13,13′), 7.10 (td, 2H, H4,4′), 7.21 (td, 2H, H3,3′), 7.24 (d, 2H, H8,8′), 7.32 (d, 2H, H11,11′), 7.51 (dd, 2H, H5,5′), 7.83 (d, 2H, H7,7′). 13C-NMR (δ, ppm): 25.68: C18,18′, 25.89: C21,21′, 28.79: C17,17′, 28.87: C20,20′, 68.24: C16,16′, 69.22: C19,19′, 112.30: C11,11′, 113.92: C2, 114.00: C2′, 116.27: C14, 116.51: C14′, 118.35: C4, 118.58: C4′, 120.53: C13,13′, 123.85: C10,10′, 127.39: C8,8′, 129.00: C3,3′, 130.98: C6,6′, 131.69: C5,5′, 139.63: C7,7′, 153.52: C15,15′, 154.53: C1,1′, 157.92: C12, 158.15: C12′, 192.93: C9,9′. 13C-DEPT-135 (δ, ppm): 25.68: C18,18′, 25.89: C21,21′, 28.79: C17,17′, 28.87: C20,20′, 68.24: C16,16′, 69.22: C19,19′, 112.30: C11,11′, 113.92: C2, 113.99: C2′, 116.27: C14, 116.51: C14′, 118.36: C4, 118.59: C4′, 120.53: C13,13′, 127.39: C8,8′, 129.00: C3,3′, 131.69: C5,5′, 139.63: C7,7′.
O), 1579.70 (C
C). 1H-NMR (δ, ppm): 1.18 (p, 4H, H18,18′), 1.42 (p, 4H, H17,17′), 1.96 (p, 4H, H20,20′), 3.76 (t, 4H, H16,16′), 4.10 (t, 4H, H19,19′), 6.75 (dd, 2H, H2,2′), 6.85 (d, 2H, H14,14′), 6.88 (d, 2H, H13,13′), 7.04 (td, 2H, H4,4′), 7.22 (td, 2H, H3,3′), 7.24 (d, 2H, H8,8′), 7.31 (d, 2H, H11,11′), 7.49 (dd, 2H, H5,5′), 7.81 (d, 2H, H7,7′). 13C-NMR (δ, ppm): 25.87: C18,18′, 26.21: C17,17′, 28.88: C20,20′, 68.27: C16,16′, 69.26: C19,19′, 112.15: C11,11′, 113.85: C2, 113.92: C2′, 116.39: C14, 116.62: C14′, 118.49: C4, 118.72: C4′, 120.68: C13,13′, 123.79: C10,10′, 127.38: C8,8′, 128.97: C3,3′, 130.98: C6,6′, 131.80: C5,5′, 139.19: C7,7′, 153.60: C15,15′, 154.54: C1,1′, 157.92: C12,12′, 192.62: C9,9′. 13C-DEPT-135 (δ, ppm): 25.87: C18,18′, 26.21: C17,17′, 28.88: C20,20′, 68.27: C16,16′, 69.25: C19,19′, 112.15: C11,11′, 113.84: C2, 113.92: C2′, 116.39: C14, 116.63: C14′, 118.49: C4, 118.72: C4′, 120.68: C13,13′, 127.38: C8,8′, 128.97: C3,3′, 131.80: C5,5′, 139.19: C7,7′.
The removal percent was calculated using the below equation:
The most significant evidence of bis-aldehyde and bis-ketone formation appears in the FTIR spectra of compounds 1a–f. This includes the disappearance of a broad band at 3450–3330 cm−1, which corresponds to the hydroxyl group of hydroxy benzaldehydes and acetophenones, a shift in the absorption band of the carbonyl group to a range of 1681–1662 cm−1, and the presence of intense peaks of CH2 stretching linkages at 2956–2833 cm−1,29 which are absent in mono-aldehydes and mono-ketones. The 1H-NMR spectroscopic analysis confirmed these findings by showing the loss of the aldehydes and the hydroxyl peak of ketones,30 the appearance of peaks of CH2 linkages at 1.5–4.1 ppm,31 and the presence of the C–H peak of aldehydes at approximately 10.5 ppm. Additionally, the 13C-NMR spectroscopic analysis revealed the carbonyl group peak at approximately 189 ppm, along with peaks of CH2 linkages at 25–68 ppm.32 The DEPT charts predicted downward peaks of CH2 linkages at 25–68 ppm and the disappearance of peaks for non-protonated carbons, including the carbonyl of acetophenone and some of the aromatic carbon atoms.
Further evidence of macrocycle formation appeared in the FTIR spectra of compounds 2a–e. This evidence included the disappearance of a band at 2760–2746 cm−1, which corresponded to the C–H stretching of bis-aldehydes, and a shift in the absorption band of carbonyl groups from a range of 1681–1662 cm−1 to the lower range of 1664–1651 cm−1.33,34 The 1H-NMR spectroscopic analysis affirmed this by showing the loss of the aldehydes' C–H peak at approximately 10.5 ppm and the disappearance of the CH3 peak of ketones at approximately 2.6 ppm.35 The 13C-NMR spectroscopic analysis further indicated a shift in the carbonyl group peak to 191–194 ppm.36,37 Predicted DEPT charts demonstrated downward peaks of CH2 linkages at 25–68 ppm and the disappearance of peaks for non-protonated carbons, including carbonyl and some of the aromatic carbon atoms.
| Macrocycle 2a | Macrocycle 2b | Macrocycle 2c | Macrocycle 2d | Macrocycle 2e | Ascorbic acid | |
|---|---|---|---|---|---|---|
| 125 ppm | 51 | 49 | 44 | 47 | 50 | 90 |
| 250 ppm | 52 | 51 | 53 | 48 | 57 | 90 |
| 500 ppm | 52 | 51 | 55 | 49 | 59 | 90 |
| 1000 ppm | 52 | 58 | 58 | 53 | 79 | 90 |
The current study established that the radical-scavenging efficacy of compounds 2a–e is fundamentally rooted in their electron-donating attributes. Dimethyl sulfoxide (DMSO), a polar solvent, was employed39 to attract and inhibit the radicals. The results differed across the various compounds and concentrations tested. Ascorbic acid, renowned for its potent antioxidant properties, was used as a standard in this investigation. Notably, compound 2e (at 1000 ppm) exhibited an antioxidant activity pattern closely resembling that of ascorbic acid, as shown in Fig. 2, with a remarkable 79% inhibition of radicals, indicating significantly lower absorbance compared to the other compounds (2a–e). At different concentrations, the remaining compounds displayed moderate free radical scavenging, exceeding 50% inhibition. However, compounds 2b (at 125 ppm), 2c (at 125 ppm), and 2d (at 125 ppm, 250 ppm, and 500 ppm) demonstrated lower inhibition of free radicals, falling below the 50% threshold.
![]() | ||
| Fig. 2 Inhibition of radicals by 2a–e at the concentration of 1000 ppm as compared to a standard of ascorbic acid. | ||
To evaluate the antibacterial activity of these macrocyclic compounds, we employed the agar well diffusion method. Notably, the evaluated compounds displayed varying inhibition zones on the culture media against both types of bacteria. This discrepancy in antibacterial activity was attributed to the diverse substituents present on the aromatic rings and linkages of these compounds, as they all share a common core chemical structure.
The comprehensive evaluation results, as presented in Table 2 and Fig. 4, revealed compelling insights. Specifically, compounds 2b (500 ppm), 2b (1000 ppm), and 2d (125 ppm) exhibited the most substantial inhibition zones against S. aureus, as shown in Fig. 5 and 6, while compounds 2a (250 ppm), 2a (1000 ppm), and 2b (500 ppm) displayed exceptional antibacterial activity against E. coli across a wide range of concentrations. Conversely, compounds 2b (250 ppm) and 2e (250 ppm) showed comparatively smaller inhibition zones against S. aureus. Compounds 2a (125 ppm), 2b (125 ppm), 2c (125 ppm), 2c (1000 ppm), 2d (125 ppm), 2d (500 ppm), 2e (250 ppm), and 2e (1000 ppm) exhibited the least significant antibacterial activity against E. coli, when compared to other macrocyclic compounds, across the entire concentration range. These results indicated that the Gram-negative bacteria E. coli displayed greater resistance in comparison to the Gram-positive bacteria S. aureus, as shown in Fig. 3.
| Concentration | E. coli (Gram-negative) | S. aureus (Gram-positive) | ||||||
|---|---|---|---|---|---|---|---|---|
| 125 ppm | 250 ppm | 500 ppm | 1000 ppm | 125 ppm | 250 ppm | 500 ppm | 1000 ppm | |
| Macrocycle 2a | 11 | 13 | 14 | 13 | 18 | 18 | 19 | 19 |
| Macrocycle 2b | 11 | 12 | 13 | 12 | 18 | 17 | 21 | 20 |
| Macrocycle 2c | 11 | 12 | 12 | 11 | 17 | 18 | 19 | 18 |
| Macrocycle 2d | 11 | 12 | 11 | 12 | 20 | 18 | 19 | 18 |
| Macrocycle 2e | 12 | 11 | 12 | 11 | 19 | 17 | 18 | 17 |
Recognizing the gravity of the problem, extensive research has been conducted to address it. In this regard, we evaluated this novel class of synthesized chalcone moiety macrocycles for their efficacy in removing colorants from wastewater, specifically at room temperature, as shown in Table 3. To assess their adsorption capabilities, 5.0 mg L−1 methylene blue was employed as the adsorbate, with compounds 2a–e serving as the adsorbents.
| Compound | Absorbance | % removed color |
|---|---|---|
| Methylene blue | 0.983 | 0.00 |
| 2a | 0.207 | 78.94 |
| 2b | 0.103 | 89.52 |
| 2c | 0.075 | 92.37 |
| 2d | 0.034 | 96.54 |
| 2e | 0.123 | 87.48 |
The results demonstrate the amazing efficiency of these chalcone moiety macrocycles in eliminating contaminants from wastewater. Notably, compounds 2c and 2d emerged as the most effective, achieving removal rates of 92.37% and 96.54% for methylene blue dye, respectively, as shown in Fig. 7 and 8, surpassing the performance of other adsorbents. In contrast, compound 2a exhibited a lower removal efficiency of 78.92%, as seen in Fig. 9. These findings signify a significant step forward in combatting water pollution and highlight the potential of chalcone moiety macrocycles to provide a sustainable solution to this critical issue.
The usefulness of the specific adsorbent depends not only on its adsorptive capacity, but also on the ease of its regeneration and reuse. Four different eluents (ethanol, methanol, nitric acid, and deionized water) were applied as the desorbing agent. The most optimal one was ethanol, and thus, the adsorbent was dried in an oven during regeneration, with each sorption–desorption cycle employing ethanol and subsequent heat treatment.
The removal efficiency of the adsorbents remained constant, and no significant difference in removal efficiency was observed during five adsorption–desorption cycles. These data are encouraging and indicate that there is satisfactory reusability for the adsorbents used in this experimental study.
The synthesized compounds demonstrated promising applications, particularly in biological activities against the Gram-positive bacteria S. aureus and the Gram-negative bacteria E. coli. Compounds 2a–e displayed effective results, with a noteworthy observation of greater susceptibility of Gram-negative bacteria (E. coli) as compared to Gram-positive bacteria (S. aureus). Comprehensive evaluation highlighted compound 2b (at 500 ppm) as a potent inhibitor against E. coli, while compound 2a (at 500 ppm) exhibited exceptional antibacterial activity against S. aureus, with the introduction of a halogen atom, such as fluorine, contributing to the enhanced performance against both bacterial types.
In addition to antimicrobial properties, the compounds demonstrated antioxidant activity, with strong antioxidant activity of 79% inhibition of radicals exhibited by compound 2e (at 1000 ppm) that was similar to that of ascorbic acid at 90% inhibition. This result, with significantly lower absorbance compared to the other compounds (2a–e), underscores the potential of these compounds in antioxidant applications.
Furthermore, the macrocycles were evaluated for their ability to remove dye from contaminated water, with all five exhibiting excellent results. Compound 2d, in particular, emerged as the most effective, achieving a remarkable 96.54% removal rate for methylene blue dye, surpassing the performance of other tested adsorbents. These findings collectively highlight the diverse and promising applications of the synthesized compounds in various fields, from antibacterial and antioxidant activities to water purification processes.
Footnote |
| † Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d3ra08133h |
| This journal is © The Royal Society of Chemistry 2024 |