Francesco
Ferlin
,
Agnese
Zangarelli
,
Simone
Lilli
,
Stefano
Santoro
and
Luigi
Vaccaro
*
Laboratory of Green S.O.C. – Dipartimento di Chimica, biologia e Biotecnologie, Università degli Studi di Perugia, Via Elce di Sotto 8, 06123 – Perugia, Italy. E-mail: luigi.vaccaro@unipg.it; Web: http://www.dcbb.unipg.it/greensoc
First published on 26th November 2020
Herein we present an efficient and regioselective iron-catalyzed methodology for the external oxidant-free functionalization of quinoline-N-oxides. The protocol, based on the use of inexpensive and easily accessible FeSO4, showed broad applicability to a wide range of substrates. An additional green feature of this synthetic methodology is H2O being the only by-product. Experimental and computational investigations provide support to a mechanism based on a facile C–H activation event. The green efficiency of the process has also been carefully assessed using: (i) metrics related to the synthetic process (AE, Yield, 1/SF, MRP and RME); (ii) safety/hazard metrics (SHZI and SHI); and (iii) metrics related to the metal used as the catalyst (Abundance, OEL and ADP). In addition to the many advantages of this protocol related to the green iron catalyst used and the safety/hazard features of the process, an E-factor value of ca. 0.92 (84 to >99% reduction compared to known protocols) evidently confirms the sustainable efficiency of the procedure presented. Practical utility has also been demonstrated by performing the reaction efficiently on a multi-gram scale.
Scheme 1 Examples of biologically active molecules with a quinoline core and features of iron-catalyzed C–H alkenylation. |
The direct C–H functionalization of quinoline-N-oxides has been mainly reported using different transition metal catalysts.4 Among these, palladium,3b,e rhodium,5 copper,6 and cobalt7 catalysts have been exploited to achieve either C2 or C8 olefination of quinoline-N-oxide, and in a unique case, C2 alkenylation has been performed using a heterogeneous catalytic system.3a In addition, alkenylation strategies also comprise metal-free or Brønsted acid catalyzed protocols.8 In recent years, there has been growing interest in the development of efficient catalytic processes based on 3d transition metals, in place of the more expensive 4d and 5d elements.9 From this perspective, iron represents an ideal choice, as one of the most abundant elements in the earth's crust and being associated with very low toxicity.10 Excellent recent contributions have reported the efficiency of iron to catalyze C–H functionalization processes, including allylation,11 alkylation,12 arylation,13 alkynylation14 and amination reactions.15 Despite these considerable advances, the iron-catalyzed C–H bond alkenylation reaction remains limited to a few examples,16 and specifically to the use of waste-producing organo-zinc or Grignard reagents, but with no possibility for direct C–H bond alkenylation. In our program aimed at the development of sustainable C–H activation reactions,17 we are also interested in the use of earth-abundant non-toxic transition metals, and in this contribution we report our result on the development of the first iron-catalyzed C2-selective alkenylation of quinoline-N-oxides (Scheme 1b). In terms of sustainability, this synthetic methodology features H2O as the sole by-product with excellent atom economy.
Entry | Solvent | Cat. | C [%] | Selectivity (3a:4a) | 3a [%] |
---|---|---|---|---|---|
a Reaction conditions: 1a (1 mmol), 2a (2 mmol), catalyst (1 mol%), solvent (50 μL, 20 M), 16 h at 100° C. b GLC conversion has been determined using samples of pure compounds as reference standards. c Isolated yield. d Degradation products have been detected. e Iron(II) phthalocyanine. | |||||
1 | Toluene | FeSO4 | 98 | 100:0 | 86 |
2 | Solvent-free | FeSO4 | 83 | 95:5 | 77 |
3 | DMF | FeSO4 | 90 | 52:48 | 30 |
4 | Dioxane | FeSO4 | 68 | 45:55 | 18 |
5 | Toluene | — | 30 | 15:85 | 9 |
6 | Toluene | FeCl3 | 95 | 52:48 | 15 |
7 | Toluene | CuSO4 | 82 | 5:95 | — |
8 | Toluene | Cu(OAc)2 | 84 | 17:83 | 13 |
9 | Toluene | Pd(OAc)2 | 56 | 60:40 | 30d |
10 | Toluene | CoSO4 | 91 | 50:50 | 23 |
11 | Toluene | BrMn(CO)5 | 98 | 25:75 | 18 |
12 | Toluene | FePce | 68 | 85:15 | 12 |
Performing the reaction under solvent-free conditions or by changing the medium to DMF or 1,4-dioxane resulted in lower yields and most importantly with lower selectivity. In fact, in the latter cases, the formation of the hydroxylated product was observed, probably derived from an alternative cycloaddition/ring opening sequence.8 Conducting the reaction without the catalyst led to very poor conversion. The use of different iron, copper, palladium, cobalt or manganese catalysts resulted in variable conversions and poor selectivities and isolated yields.
With the optimized reaction conditions in hand, we explored the reaction scope (Scheme 2) by reacting a variety of quinoline-N-oxides (1) with different acrylates (2).
Gratifyingly, quinoline-N-oxides containing either electron-donating or electron-withdrawing groups were olefinated regioselectively in good yields. Substitution at the C6 and C8 positions by either methoxy or hydroxy groups and 4,7-dichlorosubstitution were tolerated, giving good results in terms of selectivity and yield. It is worth noting that methoxy, chloride, and hydroxy groups are versatile functionalities that allow further transformations. Also, changing the alkyl substituent on the acrylate only resulted in marginal differences in product yields.
Next, we investigated whether the methodology is compatible with different alkenes, other than acrylates. Indeed, the reaction is very efficient with substituted or unsubstituted styrene derivatives, showing also in this case excellent compatibility with different functionalities present on quinoline-N-oxide; in this protocol, acid labile substrates (6m and 6n) have also been obtained in excellent yields (Scheme 3).
Furthermore, the methodology also enabled the direct alkenylation of isoquinoline-N-oxide, with an excellent level of selectivity, allowing to obtain 1-styrylisoquinoline 6k. Notably, this iron-catalyzed process has been found to allow the direct alkenylation of quinoxaline-N-oxide 7, and the methodology herein reported offers, to the best of our knowledge, a very rarely explored and step economical access to C2-functionalized quinoxalines (Scheme 4).
The practical usefulness of the methodology is also demonstrated by its prompt scalability, which allowed us to perform multigram-scale reactions on two different substrates, further improving the associated yields (Scheme 5).
Mechanistic studies of iron-catalyzed reactions are particularly challenging, for both experimental and computational methods. Intrigued by the efficiency of the proposed methodology, we decided to investigate its mechanism (Scheme 6). First, we heated substrate 1a in D2O in the presence of 1 mol% of the catalyst, observing an almost complete deuteration of C2 in 5 hours (Scheme 6a). This result suggests that the C–H activation event should be relatively fast. Next, we measured the deuterium kinetic isotope effect of the reaction by subjecting 1a and the completely deuterated analogue 1ad7, either in separate reactions or in one pot, to the optimized reaction conditions (Scheme 6b and c). In both cases, we obtained KIE ≈2.1. Overall, these results are compatible with a mechanism involving a relatively fast and reversible C–H activation step preceding an irreversible rate-determining step.19 Furthermore, we also conducted the reaction between 1a and 2a in the presence of 1 equivalent of TEMPO and under otherwise standard reaction conditions (Scheme 6d). The alkenylation product 3a was formed in very small amount (12%), with the major product being quinoline 1a′. This might indicate that the inhibiting effect of TEMPO is exerted through a cleavage of the directing group, rather than through an inhibition of a radical pathway.
To gain more insight, we also studied the complete reaction mechanism by means of DFT calculations (see Scheme 7 and the ESI†). The most energetically favorable pathway involves a reversible ligand-promoted C2 deprotonation mediated by sulfate (TS1C2), followed by the oxidation of iron, a plausibly rate-determining insertion of the olefin into the C2–Fe bond (TS2C2) and a final H-abstraction to regenerate the double bond (TS3C2). Very importantly, this mechanistic proposal is also able to account for the experimentally observed regioselectivity, since the pathway for the reaction to occur on C8 is associated with significantly higher energy barriers. Furthermore, our DFT calculations suggest that alternative mechanistic scenarios involving an initial [3 + 2] cycloaddition8 are associated with significantly higher energy barriers, essentially ruling out this possibility for the present reaction (additional details are available in the ESI†).
Finally, we analyzed in depth the greenness of our protocol by using radial polygons (Fig. 1).
We carefully assessed three categories of metrics: (i) metrics related to the synthetic process (AE, Yield, 1/SF, MRP and RME); (ii) safety/hazard metrics (SHZI and SHI); and (iii) metrics related to the metal used as the catalyst (Abundance, OEL and ADP).
First of all, it is worth noting that our protocol has an associated E-factor value of 0.92 which is very low compared to other protocols available in the literature (an 84–>99% reduction considering values from 6 to 37 of catalyst-free protocols to 131–457 of palladium-catalyzed protocols, see the ESI†). This result is evidently due to the use of highly concentrated conditions and to the small amount of the solvent needed for the work-up procedure. As a consequence, the other mass-related metrics also support the efficiency and greenness of the process.
Furthermore, analyzing the safety/hazard metrics, we found that the safety hazard index (SHZI) related to the input and to the excess of starting materials, which finally results in waste, is, in the case of our protocol, the lowest resulting in an optimal Safety Hazard Impact (SHI) for the newly developed process.
These results and also the green features of iron, the metal used as the catalyst, reported in Table 2, strongly support the sustainability of the green iron-catalyzed process, indeed with iron being decisively more abundant in the earth's crust compared to palladium and its very low depletion (ASP).
Catalyst | Metal abundance (%) | RPP | OEL (mmol m−3) | ADP |
---|---|---|---|---|
RPP: risk phrase potential; OEL: occupational exposure limit; ADP: abiotic resource depletion. | ||||
FeSO4 | 5.6 | 1.56 | 0.17 | 0.00035 |
PdOAc2 | 0.015 | 1.73 | 0.004 | 0.32 |
PdCl2 | 0.015 | 1.85 | 0.004 | 0.32 |
In addition, by combining the toxicity data present in the literature (exposure limits, risk phrases and acute toxicity), the expected reduced hazard impact of iron compared to palladium can be quantified.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/d0gc03351k |
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