Dace
Rasina
a,
Arianna
Kahler-Quesada
a,
Simone
Ziarelli
a,
Svenja
Warratz
b,
Hui
Cao
b,
Stefano
Santoro
a,
Lutz
Ackermann
*b and
Luigi
Vaccaro
*a
aLaboratory of Green Synthetic Organic Chemistry, CEMIN – Dipartimento di Chimica, Biologia e Biotecnologie, Università di Perugia Via Elce di Sotto, 8, 06123 Perugia, Italy. E-mail: luigi.vaccaro@unipg.it
bInstitut für Organische und Biomolekulare Chemie, Georg-August-Universität Göttingen, Tammannstrasse 2, 37077 Göttingen, Germany. E-mail: lutz.ackermann@chemie.uni-goettingen.de
First published on 9th June 2016
Herein, we report the unprecedented use of a heterogeneous palladium catalyst for the step-economical Catellani reaction. The substrate scope with encapsulated Pd(OAc)2 (Pd EnCat™ 30) or Pd/Al2O3 proved to be broad, while the renewable biomass-derived γ-valerolactone (GVL) was identified as an effective reaction medium. Mechanistic studies highlighted the possible heterogeneous nature of the Pd/Al2O3 catalyst, while showing that the reaction performed in the presence of Pd EnCat™ 30 is most likely catalysed by leached homogeneous palladium species. The heterogeneous Pd/Al2O3 catalyst can be easily recovered at the end of the reaction and efficiently reused in consecutive reaction runs.
Thus far, the vast majority of C–H functionalization reactions have relied on homogeneous transition metal catalysis. Only recently the attention has shifted to the use of versatile heterogeneous catalysts for C–H activation chemistry.4 However, to the best of our knowledge, examples of heterogeneous metal-catalysed Catellani reactions have as of yet proven elusive. It is particularly noteworthy that the use of heterogeneous catalysts offers great advantages as compared to homogeneous catalysts, especially in terms of recoverability of the catalysts, ease of purification and minimization of metal contamination.
Thus far, the Catellani reaction has largely been conducted in polar aprotic solvents, such as DMF, DMA or acetonitrile. These solvents, particularly DMF and DMA, present major issues related to their toxicity, and their substitution is highly desirable, especially for large-scale applications.5 Acetonitrile is typically considered the “greenest” option among polar aprotic solvents.6 However, this actually represents a rather poor alternative due to its volatility and toxicity.7
γ-Valerolactone (GVL), is a renewable biomass-derived chemical featuring high polarity, high boiling point, and good stability towards bases and acids. Only few applications employing GVL as reaction media have been disclosed.8 Recently, we have reported for the first time that GVL can be used as an environmentally-benign alternative to common toxic polar aprotic solvents.8i–k In some cases we have also observed that the use of GVL in combination with a heterogeneous catalyst lead to lower product contamination by the metal, compared to the same reaction performed in common polar aprotic solvents.8i–k This is particularly relevant since metal contamination represent a major issue in the synthesis of pharmaceutical compounds.9,10
In this article we report the first example of a Catellani reaction catalysed by a heterogeneous palladium species. The reaction is performed in a sustainable reaction media (GVL) and the optimal catalyst can be easily recovered and reused for consecutive reaction runs. Experimental mechanistic investigations were also conducted in order to clarify the nature of the catalytically active species.
Entry | Palladium catalyst | Reaction medium | Yieldb (%) |
---|---|---|---|
a Reaction conditions: 1a (0.330 mmol), 2a (0.195 mmol), norbornene (0.127 mmol), K2CO3 (0.340 mmol), [Pd] (5 mol%), reaction medium (3.75 mL). b Isolated yields. c PPh3 (15 mol%). | |||
1 | Pd EnCat™ 30 | GVL | 93 |
2 | Pd EnCat™ TPP30 | GVL | 92 |
3 | Pd/C | GVL | 94 |
4 | Pd/C, TPPc | GVL | 82 |
5 | Pd/C, PS-TPPc | GVL | 87 |
6 | Pd/Al2O3 | GVL | 95 |
7 | Pd/Al2O3 | DMF | 82 |
8 | Pd/Al2O3 | NMP | 58 |
9 | Pd/Al2O3 | MeCN | 20 |
The effect of different bases – both organic and inorganic – on the reaction was also investigated, with K2CO3 giving the best results (see ESI†).
Next, we explored the scope of the reaction between methyl 2-iodobenzoate (1a) and several olefins 2. We chose to conduct all reactions with Pd EnCat™ 30 as well as Pd/Al2O3, in order to investigate possible differences in reactivity between these two rather diverse heterogeneous catalysts. Generally, both catalysts performed well, providing the expected products in moderate to very good yields. In several cases Pd EnCat™ 30 gave slightly better results in terms of yields than Pd/Al2O3. α,β-Unsaturated esters and ketones (2a–c) were efficiently converted to the product by either of the two catalytic systems in yields ranging from 60% to 95% (Tables 2 and 3, entries 1–3). Acrylonitrile (2d) furnished good results in the reaction catalysed by Pd EnCat™ 30 (Table 2, entry 4), while much lower yield was obtained using Pd/Al2O3, which also needed longer reaction times (Table 3, entry 4).
Entry | 2 | R1 | R2 | Time | Yieldb (%) |
---|---|---|---|---|---|
a Reaction conditions: 1a (0.330 mmol), 2a (0.195 mmol), norbornene (0.127 mmol), K2CO3 (0.340 mmol), [Pd] (5 mol%,), GVL (3.75 mL).
b Isolated yields.
c Product deriving from the ether hydrolysis and subsequent keto/enol tautomerization.
d 1.6![]() ![]() |
|||||
1 | 2a | CO2Me | H | 24 h | 93 (3a) |
2 | 2b | CO2nBu | H | 24 h | 73 (3b) |
3 | 2c | COMe | H | 24 h | 77 (3c) |
4 | 2d | CN | H | 24 h | 68 (3d) |
5 | 2e | OnBu | H | — | — |
6 | 2f | OEt | H | 24 h | 48c (3f) |
7 | 2g | Ph | H | 24 h | 63 (3g) |
8 | 2h | p-AcO-C6H4 | H | 24 h | 79d (3h + 3′h) |
9 | 2i | p-Cl-C6H4 | H | 24 h | 68 (3i) |
10 | 2j | CO2Me | Me | 2 d | 50 (3j![]() ![]() ![]() ![]() |
11 | 2k | CHO | Me | 24 h | 68 (3k![]() ![]() ![]() ![]() |
Entry | 2 | R1 | R2 | Time | Yieldb (%) |
---|---|---|---|---|---|
a Reaction conditions: 1a (0.330 mmol), 2a (0.195 mmol), norbornene (0.127 mmol), K2CO3 (0.340 mmol), [Pd] (5 mol%,), GVL (3.75 mL).
b Isolated yields.
c As a 1![]() ![]() |
|||||
1 | 2a | CO2Me | H | 24 h | 95 (3a) |
2 | 2b | CO2nBu | H | 3 d | 60 (3b) |
3 | 2c | COMe | H | 24 h | 68 (3c) |
4 | 2d | CN | H | 3 d | 32 (3d) |
5 | 2e | OnBu | H | 2 d | 40 (3e) |
6 | 2f | OEt | H | — | — |
7 | 2g | Ph | H | 24 h | 74 (3g) |
8 | 2h | p-AcO-C6H4 | H | 24 h | 54c (3h + 3′h) |
9 | 2i | p-Cl-C6H4 | H | 24 h | 86 (3i) |
10 | 2j | CO2Me | Me | 7 d | 41 (3j![]() ![]() ![]() ![]() |
11 | 2k | CHO | Me | 3 d | 57 (3k![]() ![]() ![]() ![]() |
Vinyl alkyl ethers (2e–f) proved to be more challenging, and the efficacy was strongly dependent on the nature of the catalyst (Tables 2 and 3, entries 5 and 6).
Moreover, the reaction conducted on vinyl ethyl ether (2f) with Pd EnCat™ 30 delivered the formyl-substituted product through a Domino Catellani reaction along with hydrolysis and keto/enol tautomerization. Styrene (2g) and para-substituted styrenes (2h–i) reacted efficiently with both catalysts (Tables 2 and 3, entries 7–9).
Interestingly, in both the reactions performed with the two catalysts, the chlorine functionality was well tolerated (Tables 2 and 3, entry 9), which should prove instrumental for further late-stage diversifications.
1,1-Disubstituted olefins were also subjected to the optimized reaction conditions with either Pd EnCat™ 30 or Pd/Al2O3 as the catalysts (Tables 2 and 3, entries 10 and 11). Their reactivity was in line with that observed for the monosubstituted olefins, with yields ranging from 41% to 68%. However, due to the presence of the methyl group on the substrate, the β-elimination step of the final Mizoroki–Heck-type reaction could occur in two positions, thus generating two isomeric products (3 and 4). As to the substitution pattern on the aryl iodides 1, the optimized palladium catalyst also enabled the synthesis of products 3l–3o (Scheme 1).
The coupling of the Catellani reaction with a terminal hydrogenolysis step provides step-economical access to meta-difunctionalized aromatic species.3,13 We tested the applicability of this strategy under the optimized reaction conditions with Pd/Al2O3 as the catalyst and benzyl alcohol as hydride donor (Scheme 2). The reaction proceeded efficiently, affording the expected coupling product 5 in high yield.
A major issue associated with transition metal catalysis, and in particular with palladium chemistry, is the nature of the catalytic active species. Indeed, it frequently was noted that operationally heterogeneous reactions actually occur through the catalysis of soluble leached metal species or, vice versa, that operationally homogeneous reactions were catalysed by in situ formed insoluble metal particles.14 This problem is also of key relevance for C–H functionalization reactions.4 It is worth considering that the actual nature of the catalyst is not only important for mechanistic reasons, but also has practical implications, since it finally controls the possibility to reuse the recovered catalyst and the metal contamination of the products. Unfortunately, assessing the nature of the catalytic active species (homogeneous vs. heterogeneous) is not a simple task. Several experiments have been proposed but none of them is able to give conclusive evidence about the mechanism. Instead, it is necessary to rely on multiple experiments in order to possibly obtain sufficient support to one of the mechanistic scenarios.14
For these reasons, we decided to investigate the nature of the catalytically active species through various approaches, for both the reactions catalysed by Pd EnCat™ 30 and by Pd/Al2O3. First, we performed a hot-filtration test by removing the solid catalyst one hour after the beginning of the representative reaction between 1a and 2a, and allowing the filtrate to stir for 3 days at 105 °C. Interestingly, the two catalysts led to quite different results. Thus, while Pd/Al2O3 gave a very low conversion (7%), Pd EnCat™ 30 furnished 3a in 37% conversion. Second, for the same reaction we performed a mercury-poisoning test for both catalysts. Again, the two catalysts behaved differently. In fact, while the addition of Hg(0) completely hampered the catalytic activity of Pd/Al2O3 with only 4% conversion after 20 hours, the reaction with Pd EnCat™ 30 gave 46% conversion under otherwise identical reaction conditions (see ESI†). These results suggest that leached palladium species might play a key role in the reaction catalysed by Pd EnCat™ 30, but not in the reaction with Pd/Al2O3.15
Third, we measured the amount of palladium leached into the crude product by inductively coupled plasma optical emission spectrometry (ICP-OES), for both catalysts, before and after aqueous work-up (Table 4). The amount of palladium leached from Pd/Al2O3 was very low, even before aqueous work-up (∼2 ppm). However, the extent of metal leaching from Pd EnCat™ 30 is relatively high (52.4 and 10.5 ppm before and after aqueous work-up, respectively), and in line with previous findings15 and with our hot-filtration and Hg-poisoning tests.
Catalyst | Palladium leaching (ppm) | |
---|---|---|
Pd EnCat™ 30 | no work-up | 52.4 |
aq. work-up | 10.5 | |
Pd/Al2O3 | no work-up | 2.2 |
aq. work-up | 0.5 |
Overall, these results suggest that the two tested catalysts exert their catalytic activity in different ways. While Pd EnCat™ 30 is proposed to catalyse the reaction by releasing homogeneous soluble palladium species, the C–H activation catalysed by Pd/Al2O3 is either genuinely heterogeneous or may proceed through a “release and catch” mechanism.16
From sustainability and chemical efficiency point of views, it is mostly important that the amount of palladium leached into the product is very low and that the solid catalyst can be efficiently reused. Therefore we tested the recyclability of Pd/Al2O3 in the reaction between 1a and 2a in GVL, by recovering the catalyst by simple filtration. The catalyst fully retained its activity for at least three reaction runs, constantly giving full conversion to the products. Thus, the reaction of substrates 1a and 2a was repeated for four consecutive runs giving the desired product 3a constantly in 93–95% yield (Fig. 1).
The solids were then separated from the solution by vacuum filtration and rinsed with cyclopentyl methyl ether. The organic layer was washed with water and dried over anhydrous Na2SO4. The products were isolated by flash column chromatography using a 4:
1 mixture of petroleum ether and ethyl acetate as the eluent.
Footnote |
† Electronic supplementary information (ESI) available: Experimental details, characterization data, and copies of NMR spectra of known (3a and 5) and new compounds (3b–3o, 3′h, 4j, 4k). See DOI: 10.1039/c6gc01393g |
This journal is © The Royal Society of Chemistry 2016 |