Jingjing Zhaoab,
Pan Lia,
Chungu Xiaa and
Fuwei Li*a
aState Key Laboratory for Oxo Synthesis and Selective Oxidation, Lanzhou Institute of Chemical Physics, Chinese Academy of Sciences, Lanzhou, 730000, China. E-mail: fuweili@licp.cas.cn; Fax: +86-931-4968129
bGraduate University of Chinese Academy of Sciences, Beijing, 100049, China
First published on 1st April 2015
A direct and eco-friendly nitration methodology to synthesize 3-nitroquinoline N-oxides from quinoline N-oxides using tert-butyl nitrite as both the nitro source and oxidant has been developed. Although this reaction undergoes a free radical process, it exhibits high regioselectivity and can be smoothly scaled up to gram scale.
Recently, direct C–H nitration of olefins and arenes has been developed rapidly. Accordingly, various nitroolefins were synthesized from olefins with different nitrating agents (Scheme 1, Route A).6 Besides, direct C–H nitration of arenes could also be realized through the following two pathways: (1) Pd, Cu or Rh-catalyzed aromatic C–H nitration with the necessary assistance of directing groups (Scheme 1, Route B);7 (2) nitration at the ortho- and para-position of phenol or amines (Scheme 1, Route C).8 Although these nitration methods have gained significant developments, the direct nitration of heterocycles has rarely been reported.
Quinoline N-oxides and quinoline derivatives exist widely in natural products, pharmaceuticals and functional materials. Generally, quinoline N-oxides9 were used as a typical substrate to realize C-2 functionalization via C–H bond activation.10 Meanwhile, the nitration of quinoline N-oxides usually proceed at the 4 or 8-position in the presence of mixed acid (Scheme 2).11,12 Comparing with the above mentioned C2- and C4-functionalization of quinoline N-oxide, the direct C3-functionalization including the nitration has rarely been achieved. Considering that the electron density of C3 position is slightly higher than that of C2 and C4 sites, it is speculated to provide a way to develop selective C3-functionalization method through electrophilic radical coupling strategy. As part of our continuing interest in free radical and the heterocyclic chemistry,13 we herein disclose our investigation on the direct C3 nitration of quinoline N-oxide using TBN as an eco-friendly nitration source under metal free conditions. Although it is known that the selectivity of free-radical transformation is difficult to control, our methodology displays excellent C3 selectivity and can be smoothly scaled up.
Quinoline N-oxide 1a was initially chosen as the model substrate to screen the various reaction parameters (Table 1). The 3-nitroquinoline N-oxide 2a was isolated in 50% yield using NaNO2 as NO2 source with the assistance of Pd(OAc)2 and K2S2O8 in MeCN (entry 1). However, only trace amount of 2a was observed in the absence of Pd(OAc)2 (entry 2). Surprisingly, when TBN was employed as the nitro source and oxidant, the desired 2a was obtained in 77% yield (entry 3). Running the reaction under oxygen or argon atmosphere made the yield decrease to 53% and 66%, respectively (entries 4 and 5). The reaction proceeded smoothly in DCE and toluene (entries 6 and 7). Unfortunately, the reaction did not work in H2O (entry 8). To be noteworthy, 94% yield could be obtained when the loading of TBN was increased to 3.5 equivalent (entry 10). In addition, decreasing the temperature brought a distinct decrease in the yields (entries 11–13), implying such reaction is quite sensitive to temperature variation.
Entry | NO2 source (equiv.) | Solvent | T (°C) | Yield (%) |
---|---|---|---|---|
a All reactions were carried out on a 0.3 mmol scale in 3 mL of solvent for 24 h. Isolated yield.b K2S2O8 (2.5 equiv.) was added.c Pd(OAc)2 (10 mmol%) was added.d Under oxygen in pressure tubes.e Under argon in pressure tubes. | ||||
1b,c | NaNO2 (2.5) | MeCN | 100 | 50 |
2b | NaNO2 (2.5) | MeCN | 100 | Trace |
3 | t-BuONO (2.5) | MeCN | 100 | 77 |
4d | t-BuONO (2.5) | MeCN | 100 | 53 |
5e | t-BuONO (2.5) | MeCN | 100 | 66 |
6 | t-BuONO (2.5) | DCE | 100 | 74 |
7 | t-BuONO (2.5) | Toluene | 100 | 72 |
8 | t-BuONO (2.5) | H2O | 100 | N.R. |
9 | t-BuONO (3.0) | MeCN | 100 | 89 |
10 | t-BuONO (3.5) | MeCN | 100 | 94 |
11 | t-BuONO (3.5) | MeCN | 80 | 74 |
12 | t-BuONO (3.5) | MeCN | 50 | 28 |
13 | t-BuONO (3.5) | MeCN | 25 | N.R. |
With these satisfactory conditions in hand, we then turned to examining the scope of quinoline N-oxides for this transformation (Table 2). Quinoline N-oxides containing electron-donating groups (OMe, Me, Ph) and electron-withdrawing groups (Br, Cl) at the 5, 6, 7, 8-positions all underwent nitration smoothly at the 3-position. 5-Bromo, 5-methoxy and 5-phenyl quinoline N-oxides gave the desired products (2b–2d) in 60–75% yields, respectively. Likewise, 6-substitued quinoline N-oxides yielded 60–82% products (2e–2i). Meanwhile, 7-methyl quinoline N-oxide afforded 2j in 64% yield. Besides, 8-substituted quinoline N-oxides still gave the desired products (2k and 2l) in moderate yields. Unfortunately, the 2,4-substituted quinoline N-oxides were not suitable for this transformation.14 No products were afforded when isoquinoline N-oxide and pyridine N-oxide were utilized as the substrates. The structure of the nitroquinoline N-oxide 2j was further confirmed by X-ray crystallography (XRD) (CCDC 1031244).
In order to prove the practicality of this approach, a gram-scale synthesis of the 3-nitroquinoline N-oxides 2a (1.36 g, 72% yield) was performed, which suggested that such methodology could also be efficiently scaled up (Scheme 3).
Furthermore, 3-nitroquinoline N-oxides 2a could be selectively reduced by PCl3 to give the corresponding 3-nitroquinoline 3a in 92% yield. Compound 2a could be hydrogenated to 3-aminoquinoline 3b in 74% yield using Pd2@NAC-800 catalyst15 under 1 atm H2 at room temperature (Scheme 4).
In order to deeply understand the mechanism, a series of control experiments were carried out (Scheme 5). The addition of either TEMPO (2,2,6,6-tetramethylpiperidinooxy) or BHT (2,6-di-tert-butyl-4-methylphenol) could stop such nitration reaction (Scheme 5, eqn (a) and (b)). The reaction was also inhibited by 1,1-diphenylethylene, and 1,1-diphenyl-2-nitroethylene was isolated in 55% yield (Scheme 5, eqn (c)).6b These results may suggest that the reaction undergo a free radical process and NO2 radical was involved in present transformation. After the reaction, tertiary butanol was detected by GC-MS, which showed that t-BuONO may generate tBuO radical and NO radical, and the latter could be easily oxidized to NO2 radical via a SET process.16
Based on the above control experiments, a plausible mechanism was proposed as shown in Scheme 6. Initially, TBN generates NO radical, which could be oxidized to NO2 radical via a SET process.5c,16 Then the NO2 radical and quinoline N-oxides generated radical A through an electrophilic radical addition process. Eventually, the desired product was generated via a single-electron oxidation process with the assistance of NO2 or tBuO radical.
In summary, we have successfully developed a direct and eco-friendly methodology for the regioselective synthesis of 3-nitroquinoline N-oxides in the absence of any metal catalyst and external oxidant. This transformation is realized due to the higher electron density of C3 position and the electrophilic property of NO2 radical. Furthermore, it is worth noting that such transformation could also be smoothly scaled up. The reactions of free radicals with other coupling partners are under investigation in our laboratory.
Footnote |
† Electronic supplementary information (ESI) available. CCDC 1031244. For ESI and crystallographic data in CIF or other electronic format see DOI: 10.1039/c5ra04632g |
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