Giulia Brufani‡
ab,
Shaomin Chen‡bc,
Maria Teresa Tiberib,
Filippo Campanab,
Emilia Paonea,
Yanlong Gu
c,
Francesco Mauriello
a and
Luigi Vaccaro
*b
aDipartimento di Ingegneria Civile, dell'Energia, dell'Ambiente e dei Materiali, Università degli Studi Mediterranea di Reggio Calabria, 89122 Reggio Calabria, Italy
bLaboratory 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: https://greensoc.chm.unipg.it
cKey Laboratory of Material Chemistry for Energy Conversion and Storage, Ministry of Education, Hubei Key Laboratory of Material Chemistry and Service Failure, School of Chemistry and Chemical Engineering, Huazhong University of Science and Technology, Wuhan 430074, China
First published on 28th January 2025
In this study, we present a waste-minimized strategy for synthesising diarylamines and triarylamines via Buchwald–Hartwig coupling. These structural motifs rank among the top 20 most prevalent functional groups in biologically active molecules, and they are widely used in fields ranging from medicinal chemistry to materials science. The heterogeneous catalyst Pd/C was effectively employed under batch conditions and packed into the reactor for the flow setup. Our waste-reduction strategy utilises an azeotropic mixture of cyclopentyl methyl ether (CPME) derived from petrochemical waste and water. To enhance process circularity, the heterogeneous catalyst, phosphine-based ligand, and CPME were recovered and reused. The use of a biphasic CPME azeotrope as the reaction medium facilitated the process under flow conditions by enabling the solubilisation of all reaction components. Final product isolation was achieved thanks to an in-line liquid–liquid separator, which allowed for a significant reduction in waste generation.
Green foundation1. This study outlines a waste-minimization strategy for synthesising diarylamines and triarylamines via Buchwald–Hartwig coupling, a widely useful and utilised synthetic tool. By employing the commercially and widely available Pd/C catalyst alongside the CPME![]() ![]() 2. The protocol has been studied and developed to adapt and be readily usable under flow conditions, allowing the reduction of waste and ensuring high efficiency. This approach significantly lowers the environmental impact while ensuring scalable and reliable production. 3. Green metrics (E-factors, RME, MRP, BI, and SHI) highlight the environmental and efficiency improvements of our method. The E-factor, reduced to 2.2–2.8, reflects the waste minimisation enabled by recycling CPME, the ligand, and Pd/C. It should also be considered that with our approach, column chromatography is no longer necessary. |
The Pd-catalysed Buchwald–Hartwig cross-coupling of amines and aryl halides to form Csp2–N bonds has become a preferred method in both basic and applied chemistry, establishing itself as the favoured technique for synthesising arylamines.3,4 Since its discovery,5–8 the scientific community has invested considerable effort in developing novel homogeneous Pd-based catalysts and phosphine-based ligands to enhance process efficiency.9,10 Despite the wide applicability of such robust Csp2–N coupling at the industrial scale,11–13 there is room for improvement in terms of its “greenness”.
With the aim of recovering valuable Pd metal catalysts and meeting the demand for isolating products with minimal Pd-contamination, the exploration of Pd-heterogeneous supported catalysts for the Buchwald–Hartwig reaction is of significant interest. This involves employing various forms of heterogeneous Pd-based catalysts such as nanocrystals and nanoparticles,14,15 as well as nanoparticles immobilised on carbon nanotubes, graphene,16–18 carbon nitrides,19 alumina,20,21 polymers,22 silica23–25 and inorganic oxide.26–29 Surprisingly, the use of readily available and commercially accessible palladium on charcoal (Pd/C) has been limited to one example that employs ferrocene-1,1′-bis-(diphenylphosphine) as a ligand.30
It is well established that flow chemistry may provide several advantages over batch synthesis, including improved safety, better scalability, process automation, and possibly reduced waste production.31–33 The major challenge in implementing the Buchwald–Hartwig coupling under flow conditions is the use of inorganic bases, which results in the formation of a stoichiometric insoluble halide salt as a by-product.34 To address this issue, sonication of the reactor channels has been proposed to prevent aggregation and reactor clogging using a homogeneous Pd-based catalyst.35,36
Highly active N-heterocyclic carbene (NHC) ligand-based homogeneous Pd-catalysts have been employed in continuous flow amination performed in a microreactor using dimethoxyethane (DME). However, the use of this solvent, with its undesired benign and safety properties and its miscibility with water, complicates the product stream and makes catalyst recovery challenging.37 Alternatively, a change of nature of the base and the use of an organic base, such as 1,5-diazabicyclo(4.3.0)non-5-ene (DBN) or 1,8-diazabicyclo(5.4.0)undec-7-ene (DBU), eliminates the formation of precipitates.38 However, such an approach has been scarcely investigated due to its limitations in applicability and economic non-viability for large-scale operations. Therefore, the identification of effective biphasic conditions could deliver an effective solution and circumvent these limitations.
Common solvents such as DME, 1,4-dioxane, and toluene, often used in Pd-catalysed Buchwald–Hartwig cross-coupling, are both hazardous and environmentally harmful. Increasing interest is therefore directed towards the use of waste-derived reaction media that offer a lower ecological footprint and effective performances.39,40 CPME has recently emerged as a viable alternative, showing favourable toxicity and safety profiles and intriguing chemical properties. It is derived from petrochemical waste via a 100% atom economical process. Moreover, possible CPME production can also be envisaged, starting from biomass and further enhancing its appeal. This solvent forms a heterogeneous aqueous azeotrope with a boiling point of 83 °C, facilitating its utilisation as a biphasic system with water.41–43
After considering all the information described above, we decided to investigate the conditions for the definition of a waste-minimised strategy to access di- and triarylamines via Buchwald–Hartwig coupling. We planned our study on the use of Pd/C as a commercial and widely accessible heterogeneous catalyst. We planned to study and compare batch and flow conditions. Our proposed strategy involved using an azeotropic mixture of CPME and water. The adoption of such a biphasic reaction medium facilitates the application under flow conditions, enabling the solubilisation of all the reaction components.
We also studied the incorporation of an in-line workup methodology, resulting in a general protocol that allows the selective extraction of the product.44 Herein, we report the final isolation of the product realised by setting up an in-line workup constituted by a liquid–liquid separator, which also allowed CPME recovery with a significant reduction of the waste generated and the recycling of the phosphine ligand used (Fig. 2).
Entry | 2a (equiv.) | Solvent | Ligand | Base | GC_Conv.![]() |
---|---|---|---|---|---|
a Reaction conditions: 1a (0.5 mmol), 2a (1.4 equiv.), Pd/C 10 wt% (1 mol%), XPhos (3 mol%), and solvent (1 mol L−1) under Ar at 110 °C for 24 h.b The conversion was determined via gas–liquid chromatography using samples of pure compounds as reference standards.c 0.5 mol L−1.d 0.7 mol L−1. EtOH = ethanol; iPrOH = isopropanol; and CH3CN = acetonitrile. | |||||
1 | 1.4 | EtOH | XPhos | NaOtBu | 60 |
2 | 1.4 | iPrOH | XPhos | NaOtBu | 50 |
3 | 1.4 | CH3CN | XPhos | NaOtBu | — |
4 | 1.4 | Toluene | XPhos | NaOtBu | 81 |
5 | 1.4 | Mesitylene | XPhos | NaOtBu | 79 |
6 | 1.4 | Xylene | XPhos | NaOtBu | 95 |
7 | 1.4 | CPME | XPhos | NaOtBu | >99 |
8 | 1.2 | CPME | XPhos | NaOtBu | >99 |
9 | 1.1 | CPME | XPhos | NaOtBu | >99 |
10 | 1.1 | CPME | XPhos | KOtBu | 94 |
11 | 1.1 | CPME![]() ![]() ![]() ![]() |
XPhos | NaOtBu | 83 |
12 | 1.1 | CPME![]() ![]() |
XPhos | NaOtBu | 80 |
13 | 1.1 | CPME![]() ![]() |
XPhos | NaOtBu | 80 |
14 | 1.1 | CPME![]() ![]() |
XPhos | KOtBu | >99 |
15 | 1.1 | Toluene![]() ![]() |
XPhos | KOtBu | 78 |
Given our interest in performing the reaction under flow conditions, the solubility of all reaction components is crucial. Therefore, we opted for a biphasic immiscible reaction mixture, which effectively solubilises both the inorganic and organic components, as well as the inorganic salt by-product, thereby preventing catalyst inhibition. Encouraged by the optimal results obtained with CPME, we tested a mixture of CPME:
H2O (50
:
50 wt%). However, a decrease in conversion was observed (Table 1, entry 11). The amount of water was decreased to the azeotropic ratio (84
:
16 wt%), but no complete conversion was obtained, even after varying the concentration (Table 1, entries 12 and 13). Using KOtBu as a base resulted in complete conversion, confirming the crucial role of the inorganic salt (Table 1, entry 14). When the reaction was performed with a toluene
:
H2O azeotrope (80
:
20 wt%), a decrease in conversion was observed (Table 1, entry 15). XPhos played a crucial role, and performing the reaction without it did not result in conversion. Moreover, we tested SPhos as a representative third-generation ligand along with various phosphine ligands from the second and first generations. The results indicate that XPhos provides the best performance, while SPhos is also active but leads to lower conversion. Ligands from the first and second generations showed significantly lower activity (see the ESI for further optimisation†). The blank experiment (without Pd/C) showed no conversion to 3a.
We also studied the reusability of Pd/C under the optimised reaction conditions (Table 1, entry 14) and observed good conversion in the 4th run and a slight decrease in conversion in the 5th run (Fig. 3). The amount of Pd-loss in each run is about 1% of the total amount used (see the ESI for further information†).
The morphology of Pd/C 10 wt% was analysed using high-resolution transmission electron microscopy (HR-TEM), energy dispersive X-ray spectroscopy (EDS), and X-ray diffraction (XRD). HR-TEM images of the fresh Pd/C catalyst reveal well-dispersed nanoparticles across the carbon support, with an average diameter of approximately 2.7 ± 0.6 nm. After the first run, an increase in nanoparticle size is observed, reaching an average of 4.6 ± 1.5 nm. Following five consecutive runs, the analysis shows that the nanoparticles begin to aggregate significantly, accompanied by a further increase in size, resulting in an approximate diameter of 7.2 ± 2 nm. This growth correlates with the decrease in conversion observed during the 5th run. The aggregation complicates the precise measurement of the average particle size. EDS correlates with the Pd distribution (Fig. 4A). The XRD patterns of fresh Pd/C and Pd/C after the 1st run show two characteristic peaks for Pd nanoparticles at 40° and 46°, reflecting the crystalline structure of Pd on the carbon support. These results, along with HR-TEM analysis, confirm that the nanometric particle size is maintained throughout the process (Fig. 4B).
![]() | ||
Fig. 4 (A) HR-TEM analysis of fresh Pd/C and Pd/C after the 1st run and 5th run, and the respective EDS analysis. (B) XRD patterns of fresh Pd/C and Pd/C after the 1st run. |
To clarify the behaviour of the catalytic system in the process, a hot filtration test at 3 h and a Hg test were conducted, both suggesting an operative heterogeneous mechanism. Microwave plasma atomic emission spectroscopy (MP-AES) analysis of the crude reaction mixture after 3 h revealed a Pd loss of 0.3% (1.5 × 10−5 mmol of Pd) in solution, coherent with the observed interruption of reactivity following both tests (see the ESI for further information†).
Aiming to minimise the waste-formation of the overall process, a careful optimisation of the workup procedure was performed. The catalyst was filtered and washed with CPME. The organic layer was extracted from the water to eliminate KBr and the excess base. CPME was distilled from the crude reaction mixture (95%), followed by the addition of cold ethanol (EtOH) to recover XPhos (91%). After distilling EtOH (95%), a pure product was obtained. The recovered solvents, CPME and EtOH, were characterised by nuclear magnetic resonance (NMR) and reused. The XPhos ligand was recovered in pure crystalline form, characterised by NMR, and reused over 10 times without any loss in efficiency. This approach allowed us to avoid purification through column chromatography.
Various aryl halides were tested under the optimised reaction conditions using our workup, and higher isolated yields were observed with bromides and iodides (Fig. 5). In this context, it should be noted that the choice of aryl halides has already been quantified in terms of its impact by life cycle assessment (LCA), showing that for variously substituted substrates, bromide and iodide can also be the overall best-balanced choices.45
The optimised reaction conditions and workup were extended to the synthesis of 19 diarylamines. Anilines with both alkyl and methoxy substituents proved to be effective starting materials and led to excellent yields (3a–3k). Anilines with electron-donating groups in conjugative positions are activated, consistent with the increased availability of the electron pair on the nitrogen, which facilitates their coordination to the metal centre. As expected, lower reactivity was observed for anilines substituted with electron-withdrawing groups, such as trifluoromethyl, or with species that can contribute to greater delocalisation of the lone pair on nitrogen (3l–3o). In these cases, it is necessary to increase the amount of catalyst, often requiring purification of the reaction product via a chromatographic column (3m, 3o, 3r and 3s). Variously functionalised aryl bromides were tested (3p–3r). The reactivity was found to be strictly related to the electrophilicity of the aryl halide. When 3-bromopyridine was used, the desired product (3r) was obtained with a moderate yield. The optimised reaction conditions were applied with N-methylaniline, obtaining product 3s with a reasonable yield.
The process was further applied to the synthesis of triarylamines from diarylamines, and N-aryl substituted carbazoles, obtaining satisfactory results in terms of isolated yield.
The only representative scale-up to 5 mmol for product 3j was achieved without any loss of efficacy, thanks to the reduced amount of Pd/C, which ensured efficient mass transfer.
To provide a more comprehensive evaluation of the applicability of the optimised protocol to various classes of amines, the process was implemented with cyclohexylamine (7a) and morpholine (7b), providing good yields of the corresponding arylamines (8a and 8b) (Scheme 1).
Aiming to increase the efficiency of the process and find conditions that allow easier scale-up and limit exposure to the reagent, a continuous flow protocol was designed using a packed reactor with a blend of Pd/C and quartz powder equipped with an appropriate back pressure regulator (BPR). An in-line continuous liquid–liquid membrane separator (Zaiput Inc.) was connected to the line to allow the recovery of CPME, which was further reused. The water in which salt KBr and the excess of the base are solubilised, therefore, represents the inevitable major waste associated with the reaction.
In continuous flow experiments, a minimal amount of sodium dodecyl sulphate (SDS) was added as an emulsifier (1 × 10−4 mol L−1) to maintain the stability of the CPME:
H2O azeotropic emulsion and to avoid any potential separation and blockage during the process.46
We investigated different conditions to optimise the flow protocol and started by using a 25 cm reactor with an internal diameter of 6 mm packed using 0.6 g of Pd/C 10 wt%. Due to the low residence time, a conversion of 11% to 3a was obtained (Table 2, entry 1). Increasing the residence time resulted in a slight increase in conversion (Table 2, entries 2 and 3). By duplicating the amount of catalyst in the blend, a substantial increase in conversion was observed (Table 2, entry 4). An increase in conversion was observed by increasing the reactor length (Table 2, entry 5) and by increasing the concentration from 0.06 mol L−1 to 0.12 mol L−1 (Table 2, entry 6). Complete conversion was observed using the conditions reported in Table 2, entry 10. These conditions enabled the quantitative conversion of 5 mmol 1a into the desired product 3a, achieving 95% yield with a productivity of 0.6 mmol h−1, while in the batch process was 0.2 mmol h−1. The complete elution required a total time of 520 minutes instead of 24 h. The reactors remained active throughout the optimisation process and substrate scope studies. The Pd content in the desired product was monitored relative to the mmol eluted, revealing a reduced value ranging from 3.6 ppm to 5.2 ppm (see the ESI for further details†).
Entry | Coil length (cm) | Pd/C (g) | Concentration (mol L−1) | Residence time (min) | Flow rate (mL min−1) | GC_conv.b (%) |
---|---|---|---|---|---|---|
a Reaction conditions: in a 0.06 mol L−1 solution of 1a (5 mmol) in CPME![]() ![]() |
||||||
1 | 25 | 0.6 | 0.06 | 30 | 1 | 11 |
2 | 25 | 0.6 | 0.06 | 40 | 0.5 | 19 |
3c | 25 | 0.6 | 0.06 | 75 | 0.5 | 23 |
4c | 25 | 1.2 | 0.06 | 100 | 0.5 | 52 |
5 | 50 | 0.6 | 0.06 | 165 | 1 | 41 |
6 | 50 | 0.6 | 0.12 | 140 | 1 | 52 |
7 | 50 | 1.2 | 0.12 | 180 | 1 | 58 |
8 | 75 | 1.2 | 0.12 | 200 | 1 | 75 |
9d | 75 | 1.2 | 0.12 | 200 | 1 | 12 |
10 | 100 | 1.2 | 0.12 | 290 | 1 | 99 (95) |
The in-line continuous liquid–liquid membrane separator connected to the flow reactor enables the recovery of product 3a and XPhos in CPME, which was then distilled and consequently reused. XPhos was precipitated from cold EtOH in a pure crystalline form and reused with no change in efficiency (96%). Then, the pure product (3a) was obtained by distilling EtOH with an isolated yield of 95% (Fig. 6).
The developed setup was applied representatively for the synthesis of products 3a, 3b, and 3j, obtaining yields higher than those of the batch process and improving the efficacy over the reaction time (Fig. 6).
At this stage, we compared various protocols reported in the literature with the optimised new batch and flow protocols for the selected product 3j. The careful optimisation of the workup procedures for both our methods significantly allowed us to reduce waste by eliminating the need for column chromatography purification and enabling the recovery of all reaction components. This allowed us to achieve E-factor values around 2–3, a remarkable improvement from the typical values in the hundreds of literature processes.21,27,47,48 The E-factors under batch (Fig. 7A, e) and flow (Fig. 7A, f) conditions were comparable, with a slight increase observed in the flow protocols due to the diluted conditions necessary to solubilise all reaction components, as reported by the E-factor profile (Fig. 7B and C) (see the ESI† for E-factor calculation details).
The well-established protocols a and b were selected to compare atom economy (AE), reaction mass efficiency (RME), material recovery parameter (MRP), stoichiometric factor (SF), benign index (BI), and safety hazard index (SHI) with our batch and flow processes.
The seven-pointed radial polygon analysis, supported by the vector magnitude ratio (VMR), demonstrated a larger area for our processes. This improvement is primarily attributed to the successful recovery of solvents and ligands, along with the avoidance of chromatographic columns, which significantly reduced the E-factor and enhanced both RME and MRP. Additionally, the SHI and BI metrics highlighted the overall environmental benefits of the optimised processes. In the flow process, a higher BI was observed due to the diluted reaction conditions, while the SHI was lower, reflecting the increased solvent usage. However, the SHI value only considers the intrinsic properties of the chemicals used. It does not account for the safety advantages of the confined reaction environment in tubes and reactors, which minimise operator exposure and enhance overall process safety (Fig. 8) (see the ESI for green metrics evaluation†).
To enhance process circularity, we optimised the workup to recover and reuse the CPME, XPhos ligand, and Pd/C catalyst. The latter was successfully recycled for 4 consecutive runs.
Additionally, the optimised workup eliminated the need for chromatographic purification, significantly reducing waste generation.
This protocol was successfully extended to the synthesis of 19 diarylamines, 6 triarylamines, and N-aryl-substituted carbazoles. Aliphatic amines were also tested.
The flow setup was designed with an in-line workup methodology, incorporating a liquid–liquid separator that enabled selective product extraction and CPME recovery. The green metrics, including E-factor, RME, MRP, BI, and SHI, demonstrated significant improvements in terms of greenness compared to well-established protocols.
Overall, the presented approach minimises waste and also provides a method for producing diarylamines and triarylamines with high efficiency and reduced environmental impact.
Footnotes |
† Electronic supplementary information (ESI) available: General procedures, full characterization of the synthesized compounds and copies of 1H, 13C and 19F NMR spectra. See DOI: https://doi.org/10.1039/d4gc06065b |
‡ These authors contributed equally. |
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