| Literature DB >> 32951124 |
Abstract
The study presents the influence of structure modulation by introducing selected donor and acceptor substituents on optical properties of benzofuran used in biological imaging. As the starting form, 2-(5-formylbenzofuran-2-yl)acetamide described experimentally was used. This molecule contains an aldehyde group as reactive site, through which conjugation with protein occurs. Structure modulation was carried out by attaching additional electron-donating and electron-withdrawing substituents to the amino group, namely -NH2, -NHCH3, -NO2, -OH, and -OCH3. Studies have shown that the -NH2, -NHCH3, -OH, and -OCH3 substituents do not induce a significant change in the position of maximum absorption and fluorescence relative to each other. They also do not change the parameters describing the nonlinear response. Only the presence of the -NO2 substituent results in significant solvatochromic shifts. Changing substituents also does not significantly affect the LD50 value, and all tested fluorescent probes should not be considered toxic to humans. Modulation of the benzofuran derivative structure also does not change the active center in which the biocomplex with the protein is formed. In each case, the conjugation takes place via LYS114. In addition, the study was prompted to analyze the linear and nonlinear optical properties of conjugates formed after the reaction with Concanavalin A.Graphical abstract.Entities:
Keywords: Benzofuran; Bioimaging; Biological activities; Conjugation with proteins; Linear and nonlinear optical properties; Solvatochromism; Toxicology
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Year: 2020 PMID: 32951124 PMCID: PMC7502069 DOI: 10.1007/s00894-020-04539-6
Source DB: PubMed Journal: J Mol Model ISSN: 0948-5023 Impact factor: 1.810
Fig. 1Structures of tested derivatives
Fig. 2The MEP surfaces for benzofuran derivatives in water. Values are given in [a.u]
Fig. 3Density difference plot in water. The purple and green lobes correspond to (ρ) and (ρ), respectively
Linear and nonlinear optical properties in water
| μGS | μCT | 〈 | Δ | 〈 | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| NH2 | 313.94 | 1.1132 | 317.10 | 9.50 | 16.31 | 396.32 | 212.90 | 96.33 | 669.93 | 0.06 | 0.00 |
| NHR | 313.98 | 0.7062 | 317.12 | 9.43 | 16.89 | 396.33 | 228.99 | 92.95 | 610.60 | 0.06 | 0.00 |
| NO2 | 314.12 | 1.0190 | 317.28 | 5.26 | 15.44 | 434.56 | 223.63 | 82.90 | 526.91 | 626.96 | 2.18 |
| OH | 314.09 | 1.0666 | 317.23 | 9.28 | 17.69 | 396.67 | 207.11 | 102.87 | 713.63 | 0.05 | 0.00 |
| OR | 344.42 | 1.0461 | 338.14 | 9.72 | 18.12 | 396.64 | 223.56 | 96.77 | 639.03 | 0.06 | 0.00 |
| NH2Con | 259.34 | 1.2824 | 258.88 | 8.01 | 13.91 | 356.88 | 233.11 | 92.48 | 0.75 | 18.05 | 0.08 |
| NHRCon | 259.44 | 1.2661 | 259.14 | 8.08 | 13.91 | 356.89 | 249.23 | 76.22 | 1.02 | 17.65 | 0.08 |
| NO2Con | 260.39 | 1.2749 | 260.64 | 2.43 | 21.68 | 412.67 | 244.02 | 72.19 | 3.31 | 1204.90 | 3.82 |
| OHCon | 259.90 | 1.1615 | 260.37 | 6.86 | 12.70 | 357.23 | 227.49 | 99.17 | 0.12 | 32.85 | 0.15 |
| ORCon | 371.08 | 1.0435 | 365.39 | 5.58 | 11.02 | 357.20 | 243.36 | 90.25 | 1.88 | 32.85 | 0.15 |
Fig. 4Theoretically determined toxicological parameters. Blue line, markers before conjugation; green line, conjugates
Fig. 5Results of the AutoDock simulations