Introduction

The catalytic society in recent days has shown significant interest and applied extensive thrust on the development of engineered heterogeneous catalysts as compared to their homogeneous analog. Their easy handling and facile isolation from the reaction mixture has made them advantageous1,2,3,4. Among them, the magnetite nanoparticles (MNPs) have acquired remarkable attention as catalyst support or as the core of nanohybrid composites to serve as a potential reusable green catalyst5,6,7. The features like easy availability, abundance, small size thereby high surface area, excellent reactivity, high biocompatibility, good magnetic permeability, presence of plenteous hydroxyl groups for surface engineering and straightforward magnetic isolation has made them a fascinating material8,9,10,11,12,13,14. However, due to high surface energy, they are highly prone to self-aggregation which reduces their catalytic activity significantly15,16,17,18. This is somewhat minimized by surface functionalization. In recent years, the biogenic green approach for synthesis of NPs has come into prominence19,20,21,22,23,24. Plants have been a ubiquitous and rich source in this regard. There are reports of using plant leaves, fruits, flowers, barks, and roots’ extract as the cheap and abundant precursors of corresponding biomolecules for functionalization25,26,27,28,29,30,31,32,33. Following the trend of our earlier report towards the bio-inspired synthesis of stable and active nanocomposite catalysts34,35,36,37,38,39,40, we demonstrate herein the Fritillaria imperialis flower as bio-resource to fabricate Fe3O4 NP. The flower is grown widely in the plateau areas of Turkey, Iraq and Iran border and Himalaya foothills (Fig. 1). The herb contains numerous phytochemicals including polyphenols, flavonoids, mild acids alkaloids and terpenoids. We further modified the biomolecule supported NPs by fabricating its exterior layer with tiny Pd NP as active catalytic phase. Finally, the catalytic application of the magnetic biogenic nanocomposite was demonstrated in the reduction of nitroarenes, a fundamental and significant chemical reaction in various organic transformations41,42. Particularly, 4-nitrophenol is a detrimental organo-pollutant in water and dreadful for all living creatures43,44. The reduced amines find wide applications in the synthesis of fine chemicals, agrochemicals, pharmaceuticals, dyes, polymers, pesticides, cosmetics and photography45,46,47,48. In view of such consequences we designed our catalyst to carry out the reduction in a facile and green chemical pathway using hydrazine hydrate (N2H4·H2O) as a mild and effective reductant. The magnetic core helps in efficient and effortless recoverability of the catalyst from the reaction mixture. Our protocol has been so proficient that a wide variety of nitro compounds has been converted to resultant amines within quick interval in aqueous ethanol producing outstanding yields and TOF.

Figure 1
figure 1

Fritillaria imperialis flower image.

Experimental

Synthesis of magnetite NPs

Following a typical co-precipitation method, a mixture of FeCl2·4H2O (2.0 g) and FeCl3·6H2O (5.2 g) were taken into deoxygenated water (25 mL) containing few drops of conc. HCl and subsequently, 250 mL of 1.5 M NaOH solution was added dropwise. The whole mixture was stirred vigorously at 60 °C. Immediately, brown colored Fe3O4 NPs were formed which were isolated using a magnetic stick. It was washed thrice with 200 mL deionized water and dried in air at 40 °C.

Preparations of Fe3O4@Fritillaria using the plant extract

0.5 gm Fritillaria flower powder was extracted into 50 mL of Milli-Q water by swirlling at 50 °C for 20 min. It was filtered over Whatman 1 paper and the filtrate was centrifuged at 4000 rpm for 5 min to precipitate out the impurities. The clear upper layer was preserved for the next step. For the preparation of Fe3O4@Fritillaria NPs, the magnetite NPs (0.5 g) were first dispersed in water by sonication for 20 min and the flower extract was added dropwise into it. The mixture was then stirred for 24 h at room temperature. Finally, the Fe3O4@Fritillaria nanocomposite was collected magnetically, washed thoroughly over DI-H2O and dried in vacuum at 40 °C overnight.

Preparation of the Fe3O4@Fritillaria/Pd NPs

Five gram of the Fe3O4@Fritillaria NPs was dispersed over deionized water (100 mL) in sonicator for 20 min. An aqueous solution of Na2PdCl4(40 mg in 20 mL H2O) was poured into dispersion and refluxed for 12 h to assure the complete reduction of Pd(II) ions. The Fe3O4@Fritillaria/Pd nanocomposite was isolated as previous, rinsed with H2O/acetone mixture to eliminate the adhered organic substances and dried likewise. The whole preparative schedule has been presented in Scheme 1. Pd content in the material was 0.08 mmol/g, analyzed by ICP-AES analysis.

Scheme 1
scheme 1

Schematic representation for the synthesis of catalyst and its application; step a: synthesis of Fe3O4@Fritillaria, step b: synthesis of Fe3O4@Fritillaria/Pd, step c: Reduction of nitroarenes over the catalyst.

Catalytic reduction of nitrobenzene

In a stirring solution of nitrobenzene (1 mmol) and Fe3O4@Fritillaria/Pd nanocomposite (0.1 mol% Pd, 13 mg) in H2O/EtOH (2:1, 3 mL), the reducing agent NH2 NH2. H2O (3 mmol) was slowly dropped and the mixture was refluxed at 80 °C. After completion (by TLC, n-hexane/EtOAc: 5/2), EtOAc was added to the reaction mixture and stirred well. After removing the catalyst over a magnet, the water in reaction filtrate was soaked over anhydrous Na2SO4. Finally, the collected organic layer was concentrated to have pure aniline in 96% yield.

Results and discussion

Catalyst characterizations and data analysis

The current work illustrates an environmental friendly and green protocol involving Fritillaria flower extract to fabricate the ferrite MNPs surface and further to introduce stable Pd NPs. The biomolecules of Fritillaria flower has a significant tendency to accumulate over Fe3O4 MNPs. The polyphenolic compounds of the flower extract contain hydroxyl and ketonic groups that chelate Pd2+ ions and subsequently reduce them green metrically (Scheme 1). The structural and physicochemical characteristics of the nanomaterial was characterized using diverse analytical techniques like FT-IR, ICP-AES, FE-SEM, TEM, EDX, XPS and VSM studies.

Figure 2 depicts comparative FT-IR spectra of bare Fe3O4 NPs, Fritillaria extract, Fe3O4@Fritillaria and Fe3O4@Fritillaria/Pd nanocomposite in order to illustrate the stepwise synthesis. In the spectrum of Fe3O4 NP (Fig. 2a), two broad peaks at 1622 and 3419 cm−1 correspond to the physisorbed H2O and the surface OH groups. The characteristic peaks appeared at 584 and 439 cm−1 are due to the stretching and bending vibrations of Fe–O bond. Pure Fe3O4 structure is characterized by a peak at 632 cm−1. Figure 2b represents the spectrum of Fritillaria extract which displays the significant peaks at 3385 cm−1 due to O–H groups of polyols49 and C-H stretching vibration from hydrocarbons and flavonoids at 2926 cm−150. Additionally, due to the presence of quinones, ketones, and carboxylic acids functions in the biomolecules contained in it, the distinctive peaks of C=O and O–C–O appears at 1709 cm−1 and 1072 cm−1 respectively51. An FT-IR band is observed in the range of 1400–1600 cm−1 owing to aromatic C=C stretching vibrations. The corresponding spectrum of Fe3O4@Fritillaria NPs is depicted in Fig. 2c. It is literally a combination of Fig. 2a,b indicating the successful functionalization of Fritillaria molecules over the ferrite NPs. These biomolecules actually perform as excellent capping agent, preventing the NPs from agglomeration and oxidation52. It also acts as reducing and stabilizing agent for immobilizing Pd NPs on the ferrite surface. The FT-IR spectrum of Fe3O4@Fritillaria/Pd NPs (Fig. 2d) is almost alike Fig. 2c except a small shift in C‒O, C=C and O‒H stretching frequencies. These shifts account for the attachment of Pd NPs on the surface modified MNPs.

Figure 2
figure 2

FT-IR spectrum of (a) Fe3O4, (b) Fritillaria extract, (c) Fe3O4@Fritillaria NPs, and (d) Fe3O4@Fritillaria/Pd NPs.

The structural morphology, size and shape of the Fe3O4, Fe3O4@Fritillaria, and Fe3O4@Fritillaria/Pd nanocomposite were investigated with the FE-SEM analysis as shown in Fig. 3. The materials are of nanometric size and of quasi-spherical shape (Fig. 3a). In addition, a continuous biopolymer layer is seen on the nanocomposite surface indicating the surface modification (Fig. 3b,c). The bright spots in Fig. 3c signifies the in situ synthesized Pd NPs being spread over the Fe3O4@Fritillaria composite.

Figure 3
figure 3

FE-SEM images of the (a) Fe3O4 NPs, (b) Fe3O4@Fritillaria NPs, (c) Fe3O4@Fritillaria/PdNPs.

EDX analysis of the material was conducted in order to know the chemical composition. The spectrum obtained on recording of signals at random points of the catalyst surface showed the presence of Fe, Pd as metallic and C, O as non-metallic components. The non metals justify the attachment of phyto-compounds in the composite (Fig. 4).

Figure 4
figure 4

EDX of the Fe3O4@Fritillaria/Pd NPs.

In addition to the EDX analysis, elemental mapping of Fe3O4@Fritillaria/Pd nanocomposite also carried out to have the knowledge of component distributions over the catalyst surface. X-ray scanning of a segment of the FE-SEM image reveals the homomorphic dispersion of all the components on the nanocomposite (Fig. 5). The uniform distribution of the active site definitely has a significant role behind its catalytic superiority.

Figure 5
figure 5

Elemental mapping of Fe3O4@Fritillaria/Pd nanocomposite.

The TEM image of the Fe3O4@Fritillaria/Pd NPs exhibits that the Pd NPs are formed with almost globular morphology (Fig. 6). As can be seen in the image (Fig. 6a), the ferrite NPs are of 10–20 nm in dimension that are coated by thin layers of Fritillaria extract. The biomolecular layers from the extract acts as the green reducing agent of the Pd ions as well as the stabilizing agent of Pd NPs. It easily detectable that the dark Pd NPs are of ~ 20–30 nm being entrapped in the modified iron oxide surface (Fig. 6b).

Figure 6
figure 6

TEM images of (a) Fe3O4@Fritillaria NPs and (b) Fe3O4@Fritillaria/Pd NPs.

Figure 7 illustrates XRD patterns of Fe3O4 and Fe3O4@Fritillaria/Pd nanocomposite. Evidently, XRD profile of the latter carries all the significant peaks that of cubic spinel Fe3O4 NPs. The XRD peaks found at 2θ = 30.3°, 35.7°, 43.4°, 53.9°, 57.4° and 62.9° can be attributed to diffraction on (220), (311), (400), (422), (511) and (440) planes respectively (JCPDS No. 19-0629). It also implies that the interior structure remains undisturbed even after bio-functionalizations and Pd anchoring. The Pd attachment can also be demonstrated by the distinctive peaks observed at 2θ = 40.1°, 46.6° and 67.9°, being ascribed to the (111), (200) and (220) crystalline planes of Pd fcc structure.

Figure 7
figure 7

XRD profile of Fe3O4 NPs and the Fe3O4@Fritillaria/Pd nanocomposite.

Magnetic characteristics of the Fe3O4@Fritillaria/Pd NPs was assessed through VSM analysis and the magnetization curve has been shown in Fig. 8. From the corresponding hysteris curve, the maximal saturation magnetization of Fe3O4@Fritillaria/Pd NPs was found to appear at 42.5 emu g−1. However, the value is much lower than bare ferrite NP (64.2 emu g−1) due to surface operations. Still, in the modified material the magnetization goes down from plateau state to zero on removal of the magnetic field which justifies it to be superparamagnetic53.

Figure 8
figure 8

Magnetism study of Fe3O4@Fritillaria/Pd NPs.

Catalytic applications of Fe3O4@Fritillaria/Pd nanocomposite

So as to explore the catalytic application of Fe3O4@Fritillaria/Pd nanocomposite and finding optimum reaction conditions, we selected the reduction of nitrobenzene as a model reaction. The effect of various conditions including temperature, solvents, catalyst load, amount of reductant and time reaction were studied over the reaction. The outcomes were documented in Table 1. Primarily, the model reaction was examined in various solvents like dimethyl formamide (DMF), EtOH, MeOH, CH3CN, H2O/EtOH and H2O. Among them, H2O/EtOH afforded the best yield and thereby selected as the optimum solvent. The amount ofFe3O4@Fritillaria/Pd nanocomposite was also explored for the model reaction. Based on the study, 0.1 mol% catalyst was the most convenient for 1 mmol of nitrobenzene. Finally, the best result for the reduction of nitrobenzene was obtained using 3.0 mmol NH2NH2·H2O as reductant and 0.013 g Fe3O4@Fritillaria/Pd (0.1 mol% Pd) catalyst respectively inH2O/EtOH (2:1) solvent at 80 °C. We also performed the reduction of nitrobenzene using the bare Fe3O4@Fritillaria NPs but only a trace of aniline was obtained. This indicates that the interaction between the Pd NPs and Fe3O4@Fritillaria is very important for catalytic success.

Table 1 Standardization of reaction conditions in the reduction of nitrobenzene over Fe3O4@Fritillaria/Pd nanocompositea.

After resolving the required optimizations, the next endeavor was to generalize them over a range of differently functionalized (electron-donating and electron-withdrawing groups) nitroarenes. The results in terms of reaction yield and TOF are shown in Table 2. All the reactions were executed superbly with all kind of substrates without noticeable influence of functional groups on the reaction. All the reactions were completed within 0.5–2 h.

Table 2 Reduction of aromatic nitroarenes catalyzed by Fe3O4@Fritillaria/Pd NPsa.

Recyclability of Fe3O4@Fritillaria/Pd catalyst

For every heterogeneous catalytic system, the isolation and recycling of catalyst is a crucial feature in view of sustainable and industrial concern. The reusability of Fe3O4@Fritillaria/Pd was examined over the reduction of nitrobenzene under optimized conditions. After finishing a fresh batch of reaction the catalyst was recovered using a bar magnet and washed several times with ethanol and water. It was regenerated after drying at moderate temperature. To our delight, we could have reused it for eight consecutive cycles of reaction without noticeable loss in its activity (Fig. 9). We further analyzed the structural morphology of Fe3O4@Fritillaria/Pd nanocomposite after recycling 7 times by using TEM and EDX. As clearly can be seen from the TEM image (Fig. 10), the catalyst retains its initial morphology and particles size without any sign of agglomeration. Alongside, there occurs no change in elemental composition as evident from EDX data (Fig. 10), which in turn validates the robustness of our material.

Figure 9
figure 9

Reusability of Fe3O4@Fritillaria/Pd catalyst for reduction of nitrobenzene.

Figure 10
figure 10

TEM and EDX data for reused Fe3O4@Fritillaria/Pd catalyst after 7 runs.

Heterogeneity test for Fe3O4@Fritillaria/Pd catalyst

The Sheldon's test was carried out to assure heterogeneous nature of the synthesized material, whether any Pd species leached out in the filtrate solution. The reduction of nitrobenzene was continued over the catalyst under optimized state for 15 min and then the reaction mixture was divided into two-halves. From one portion of the reaction mixture the catalyst was removed by a magnetic bar and both the part reactions were further continued for another 15 min. On gas chromatographic analysis, it was revealed that no significant progress in reaction was achieved under non-catalytic conditions (60% conversion) while the other portion leaded to completion. The result is shown in Fig. 11. This further suggests that there was hardly any leaching of Pd NPs took place in the reaction mixture justifying its true heterogeneity.

Figure 11
figure 11

Hot filtration and leaching test of Fe3O4@Fritillaria/Pd in the reduction of nitrobenzene.

Study of reaction mechanism

Based on earlier published works, a probable reaction pathway has been documented in Scheme 254,55,56,57. The reaction goes through several intermediates. At the outset, hydrazine gets adsorbed on the surface of Pd NPs (I) which subsequently generates N2 and nascent hydrogen by bond cleavage. This hydrogen is captured by the active Pd NPs to form metal hydride (II). In the meantime the substrate nitroarenes also get adsorbed over the catalyst surface and gets reduced by hydride transfer from II to form active nitroso derivative (III). This moiety is then further reduced to amine via hydroxylamine (IV) intermediate through hydrogen transfer. The hydrogenation of hydroxylamine is considered to be slow and rate determining step. Finally, the desired product leaves behind the catalyst surface to be used for the next cycle.

Scheme 2
scheme 2

Reaction mechanism for the reduction of nitrobenzene over Fe3O4@Fritillaria/Pd catalyst.

Uniqueness of our result

The individuality of our protocol was affirmed by comparing the catalytic performance between our methodology and the reported procedures in the reduction of 4‐nitrophenol. The results are shown in Table 3 which evidently displays that the Fe3O4@Fritillaria/Pd nanocomposite is much superior to others in terms of reaction time and yield.

Table 3 Catalytic comparison in the reduction of 4-nitrophenol.

Conclusion

We introduce a facile procedure for the synthesis of a heterogeneous and reusable Pd NPs decorated on Fritillaria imperialis flower extract modified magnetic ferrite nanoparticles by post functionalization approach. Catalytic performance of the Fe3O4@Fritillaria/Pd nanocomposite material was studied in the competent reduction of nitroarenes without the use of any added base. The protocol worked proficiently using hydrazine hydrate as the reducing agent under eco-friendly conditions affording various aromatic amines with excellent yields. In addition, due to strong magnetic nature, the Fe3O4@Fritillaria/Pd nanocatalyst could be reused as much as eight cycles in the reduction process emphasizing its true heterogeneity. In view of the outstanding catalytic behavior, the engineered material is anticipated to be a versatile support to feed many other noble metals like Ag, Au, Cu etc. towards many catalytic transformations and might find an excellent exposure in chemical industry.