Subscriber access provided by Kent State University Libraries
Photocatalytic CO2 reduction by Re(I) polypyridyl complexes immobilized on niobates nanoscrolls Leandro A Faustino, Breno L Souza, Barbara N Nunes, Anh-Thu Duong, Fabian Sieland, Detlef W. Bahnemann, and Antonio Otavio Toledo Patrocinio ACS Sustainable Chem. Eng., Just Accepted Manuscript • DOI: 10.1021/ acssuschemeng.7b04713 • Publication Date (Web): 22 Mar 2018 Downloaded from http://pubs.acs.org on March 23, 2018
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Photocatalytic CO2 reduction by Re(I) polypyridyl complexes immobilized on niobates nanoscrolls
Leandro A. Faustino1, Breno L. Souza1, Barbara N. Nunes1, Anh-Thu Duong2, Fabian Sieland2, Detlef W. Bahnemann1,3, Antonio Otavio T. Patrocinio1,2*
1
Laboratory of Photochemistry and Materials Science, Insititute of Chemistry, Universidade Federal de Uberlandia,Uberlandia, Brazil
2
3
Institute of Technical Chemistry, Leibniz University Hannover, Hannover, Germany
Laboratory “Photoactive Nanocomposite Materials”, Saint-Petersburg State University, Saint-Petersburg, Russia
* to whom the correspondence should be addressed:
[email protected] 1 ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 2 of 41
Abstract Immobilization of Re(I) CO2 reduction photocatalysts on metal oxide surfaces is an interesting approach to improve their stability and recyclability. In this work, we describe the photocatalytic activity of two Re(I) complexes (fac[Re(NN)(CO)3(Cl)], NN = 4 4-dicarboxylic acid-2 2-bipyridine, 1, or 5,6-dione1,10-phenantroline, 2) on the surface of hexaniobate nanoscrolls. After adsorption the turnover number for CO production (TONCO) in DMF/TEOA of 1 was increased from 9 to 58, which is 20% higher than that observed on TiO2, being among the highest reported values for a Re(I)-based photocatalyst under visible light irradiation without any sensitizer. The complex 2 is inactive in solution under visible light irradiation, but has a TONCO of 35 when immobilized on hexaniobate nanoscrolls. Transient absorption spectroscopy studies reveal that the slow back electron transfer and the higher reducing power of the hexaniobate conduction band electrons play a major role for the photocatalytic process. The results provide new insights concerning the role of the metal oxide substrate on Re(I)-based molecular systems for CO2 reduction.
Keywords: photocatalytic CO2 reduction; Re(I)-based molecular catalysts; layered materials; transient absorption spectroscopy
2 ACS Paragon Plus Environment
Page 3 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Introduction Artificial photosynthetic systems able to reduce CO2 into useful chemicals, such as CO, and fuels, e.g. CH4, have been intensively investigated due to the growing concerns about the consequences of CO2 accumulation in the atmosphere. The possibility to sustainably convert CO2 into CO using solar radiation is a very attractive pathway to mitigate the concentration of this greenhouse gas in the atmosphere and also provides a green source for CO, an important chemical feedstock to form syngas
1
and to feed industrial processes
based on the Fischer-Tropsch chemistry. Different photo- or photoelectrocatalysts for CO2 reduction have been reported based on metals and semiconductors 2-4, immobilized enzymes 5, 6 and coordination compounds
7-9
with large variability in terms of selectivity and
stability. While metals and semiconductors exhibit great stability but poor selectivity, enzymes and metal complexes can selectively convert CO2 into CO, but they lack from long term stability. One simple and relatively robust catalyst for CO2 reduction into CO is based on Re(I) complexes of general formula fac[Re(CO)3(NN)(L)], NN = polypyridyl ligand, L = leaving group (typically Cl- or Br-) 10, 11
. These species are one of the few examples of mononuclear complexes
able to work simultaneously as light harvester and catalyst. As a drawback, in these conditions, they exhibit low stability and poor absorption of solar radiation. For example, the highest reported turnover number (TONCO) for fac[Re(CO)3(bpy)(Cl)] is 30 in a DMF/triethanolamine (TEOA) mixture (λ>400 nm) 12
. Since the first reports concerning the photo and electrochemical activity
of these compounds for CO2 conversion
12-14
, a great number of studies have
3 ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 4 of 41
appeared in the literature with improved TONCO and the turnover frequencies (TOF). Successful strategies include variations of the polypyridyl ligand combination with sensitizers 28
22-25
15-21
and optimization of the reaction conditions
,
26-
. One interesting approach involves the immobilization of the homogeneous
Re(I) catalyst in suitable substrates, enabling the heterogenised system could be easier recycled and used in different solvents or reaction conditions
29-37
.
Windle and co-workers have shown that the immobilization of the phosphonated derivative fac-[Re(CO)3(P-bpy)(Br)], P-bpy = 2,2’-bipyridine-4,4’-bisphosphonic acid, on TiO2 leads to an increase of the TONCO from 2 to 52 in DMF/TEOA (λ>420 nm) 37. This enhancement was attributed to an increase in lifetime of the reaction intermediates due to the electron injection into TiO2. Later, Abdellah and co-workers performed a detailed investigation of the system based on timeresolved infrared spectroscopy and proposed a reaction mechanism for the TiO2 immobilized Re(I) catalyst in DMF/TEOA
38
. The authors concluded that
the improved photocatalytic efficiency of the Re(I) catalyst upon immobilization onto TiO2 is due to the slower charge recombination and the high oxidative power of the ReII species after electron injection as compared to the metal-toligand charge transfer (MLCT) state of the unbound Re(I) species. The authors proposed that during the catalytic cycle, a fraction of the injected electrons could catalytically reduce the reaction intermediate [ReI(P-bpy)(CO)3(CO)]+ in order to promote the CO release. In this work, we report the substitution of TiO2 nanoparticles by hexaniobate nanoscrolls (KxH(4-x)Nb6O17) as suitable substrates for the immobilization of Re(I)-based molecular catalysts for CO2 reduction. The hexaniobates exhibit a more negative conduction band energy (E0CB ≈ -0.75 V
4 ACS Paragon Plus Environment
Page 5 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
vs NHE
39, 40
) in relation to TiO2 (E0CB ≈ -0.3 V vs NHE
40
), increasing the
reducing ability of the injected electrons. Moreover, its scrolled lamellar morphology can favor the electron mobility in relation to TiO2 nanoparticles by promoting a vetorial charge transfer through the individual layers, which avoid ohmic losses due to grain boundaries
41
. Two different Re(I) complexes were
evaluated as photocatalysts and the results provide new insights regarding the role of the semiconductor and the anchor group on the photocatalytic efficiency of immobilized Re(I) complexes.
Experimental Section [ClRe(CO)5], 1,10-phenanthroline, 4,4’-dicarboxylic acid-2,2’-bipyridine (dcbH2), tetrabutylammonium hydroxide (TBAOH), DMF, TEOA and K2CO3 from Aldrich, Nb2O5 from “Companhia Brasileira de Metalurgia e Mineração” (CBMM) and TiO2 (Hombikat UV 100) from Sachtleben GMBH were used without any further purification. All solvents employed were HPLC grade. Syntheses. fac-[ClRe(CO)3(dcbH2)] (1) was modifications to literature procedures
prepared with some
42, 43
. 0.19 g (0.5 mmol) of [ClRe(CO)5]
and 0.11 g (0.6 mmol) of dcbH2 were suspended in 10 mL of ethanol and the mixture was heated to reflux for 7 h. The crude product precipitated as an orange solid, which was collected by filtration. Recrystallization was performed by suspending the solid in 90 ml of acetone. The unreacted polypyridyl ligand was removed by centrifugation (5000 rpm, 20 min) and then, hexane was employed to precipitate the product from the bright orange supernatant. Yields 70%. Anal. Calc. for ReC15H8N2O7Cl: C, 32.76%; H, 1.47%; N, 5.09%; Found:
5 ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 6 of 41
C, 32.40%; H, 1.98%; N, 5.27%. 1H NMR ((CD3)2CO δ / ppm) 10.04 (dd, 2H); 9.78 (s, 2H); 8.92 (dd, 2H). The ligand phdo (5,6-dione-1,10-phenantroline) was synthesized as previously reported
44, 45
. The fac-[ClRe(CO)3(phdo)] complex (2) was prepared
also following a methodology reported in the literature
46-49
. Briefly, 0.45 g (1.24
mmol) of [ClRe(CO)5] and 0.42 g (2.00 mmol) of phdo were dissolved in 20 mL of toluene and the mixture was heated to reflux for 5 h under argon atmosphere. The
product
was
collected
by
filtration
and
recrystallized
from
dichloromethane/n-hexane. Yields 60%. Anal. Calc. for ReC15H6N2O5Cl: C, 34.92%; H, 1.17%; N, 5.43%. Found: C, 34.75%; H, 1.24%; N, 5.44%. 1H NMR (DMSO-d6 δ / ppm) 9.26 (d, 2H); 8.71 (d, 2H); 7.88 (t, 2H). Bulk K4Nb6O17⋅3H2O was prepared by a solid state method
50, 51
. Nb2O5
and K2CO3 in a molar proportion of 2:3 were grinded and heated at 1,100 ºC for 10 h. The final product was washed with deionized water and then dried at 80ºC. The bulk material was then submitted to an acid treatment to partially exchange K+ cations by protons. 3.0 g of K4Nb6O17⋅3H2O were stirred in 150 mL of 0.2 mol L-1 H2SO4 during 3 days. The solid was subsequently separated by filtration, washed with water and dried at 80ºC. The hexaniobate nanoscrolls were obtained by exfoliation of bulk K4-xHxNb6O17 (0.5 g) with 100 mL of 8x10-3 mol L-1 tert-butylammonium hydroxide during seven days
52, 53
. After the stirring
is stopped the non-exfoliated materials tend to precipitate, while the exfoliated layers remain as a stable suspension. The suspension was collected and few drops of HNO3 were added to promote the precipitation of the hexaniobate
6 ACS Paragon Plus Environment
Page 7 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
layers. The final powder were collected by filtration, washed with water and ethanol and dried at 80 ºC overnight. The immobilization of the Re(I) complexes on the surface of the niobates was carried out by suspending 300 mg of the nanoscrolls in plain water (pH = 6.8). Under constant stirring, a given amount of 1 or 2 previously dissolved in ethanol was added to the niobate suspension, which was kept under stirring for 3 hours. Two different concentrations were employed for each complex: 90 µmol g-1 and 35 µmol g-1. After adsorption, the powder was recovered by centrifugation, washed several times with ethanol and acetone, and, finally, dried under vacuum overnight. For comparison, the same procedure was adopted to immobilize the complexes on Hombikat UV100 anatase TiO2 particles (SBET = 220 m2 g-1). The amount of complex adsorbed at each condition was determined spectroscopically by analyzing the remaining concentration in the supernatant after the solid removal. Methods. Electronic absorption spectra were recorded on a double beam Shimadzu UV-1650 spectrophotometer equipped with an integrating sphere. Barium sulfate was used as reference. 1H NMR spectra were recorded on a DRX-400 MHz Bruker Ascend 400 spectrometer and the residual solvent signals were used as internal standard. Attenuated total reflectance infrared (ATR-FTIR) spectra were recorded using a Perkin-Elmer Frontier spectrometer. The measurements were performed in a diamond crystal plate, using 32 scans at a resolution of 2 cm-1. X ray diffractograms were obtained using a Shimadzu XRD-6000 diffractometer, with a CuKα (λ = 1.54148 nm) monochromatic source. Specific surface area measurements were determined recording N2 adsorption/desorption isotherms using the BET methodology
54
and a 7
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 8 of 41
Quantachrome NOVAtouch LX1 surface analyzer. X ray photoelectron spectroscopy was carried out in a Leybold Heraeus analyser equiped with an Al non monochromatic X ray source and a hemispherical electron energy analyzer. The beam energy was 1484 eV and the residual C1s peak at 284.6 eV was used as internal standard. Transmission electron microscopy images were obtained in a Tecnai G2 F20 TMP (FEI Company) at 200 kV acceleration voltage. Transient absorption spectroscopy (TAS) was carried out employing a LKS80 nanosecond laser flash photolysis spectrometer (Applied Photophysics) equipped with the proper diffuse reflectance accessory as described previously 55
. The samples were placed in a closed quartz cuvette, purged with N2 and
were excited with a 420 nm laser beam (2.4 mJ cm-2 per pulse). The pump beam was produced by an optical parametric oscillator (OPOTEK) pumped by a Nd:YAG laser (Quantel; Brilliant B; third harmonic, 355 nm). The transient signals were collected by a PMT (Hammatsu R928) connected to a DSO9064A oscilloscope (Agilent). The transient decay is presented as the variation in the reflectance (∆J), which is calculated according to Equation 1
56
, where I0 is
incident intensity of the analyzing light; J0 is the diffuse reflected light without laser pulse (ground light level); Jx is the diffuse reflected light with the laser pulse. It has been reported that the ∆J value can be correlated to the transient absorption provided that ∆J is less than 0.3
57, 58
, thus to describe the results
obtained by the detection of the diffuse reflected light, the term transient absorption will be used here.
∆ =
/ / /
=
(1)
8 ACS Paragon Plus Environment
Page 9 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Photocatalytic studies. CO2 photoreduction experiments were carried out in a closed double-jacket glass reactor with total volume of 75 mL. The reactor was loaded with 28 mg of the photocatalysts suspended in 50 mL of 5:1 DMF/TEOA. The mixture was then purged with CO2 until saturation and exposed to a 300W Xe lamp equipped with a water filter and a 420 nm cutoff filter. The reactor was kept at 25º C degrees by using a water circulator system. At given time intervals, 500 µL of headspace atmosphere were sampled using a gas-tight syringe and analyzed using a quadrupole mass spectrometer for gas analysis (Hiden HPR-20)
59, 60
. The system was calibrated by injection of
different amounts of CO (m/z = 28; sensitivity 1.05) into the reactor filled with the same amount of solvent employed in the photocatalytic assays and saturated with CO2. The headspace was then sampled and analyzed by mass spectroscopy. During the assays, the O2 levels were also monitored in order to possibly detect air contamination inside the reactor, which can directly influence the CO quantification since N2 and CO are isobaric. The signals coming from eventual N2 contamination were subtracted from the raw signals obtained at m/z=28 using the 4:1 ratio in relation to the main O2 signal at m/z=32 (sensitivity 1.0). The initial signal at m/z = 28 related to CO2 fragmentation or eventual CO present in the CO2 gas bottle was also subtracted from the signals collected during the photoreaction.
Results and discussion The as-synthesized K4Nb6O17 exhibits typical lamellar structure as confirmed by XRD, Figure 1. The diffraction peaks can be indexed according to the JCPDS 21-1297 crystallographic sheet corresponding to K4Nb6O17.3H2O. 9 ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 10 of 41
The strong peaks at low angle (020, 040, 060) are characteristic for the lamellar structure, in which asymmetrical [Nb6O17]4- layers composed by edge- and corner-shared NbO6 octhaedra are stacked 61. As expected, after exfoliation the intensity of these peaks is strongly reduced as the stacked structure is lost and the layers are randomly organized. Nevertheless, the (040) diffraction peak can still be observed, which is an indication that some re-ordering along the stacking axis of K4Nb6O17 occurs when the unilamellar colloid is precipitated as nanoscrolls
62
. The strongest diffraction peaks at 2θ = 23.5 and 27.5º can be
ascribed respectively to the (220) and (002) reflections thus confirming that the in-plane crystalline order within the individual nanoscrolls persisted after the exfoliation 62-64. SEM images of the as-synthesized powder, Figure 2a, allow the visualization of the initial stacked layers. After treatment with TBA(OH) solution, the layers are separated from each other and tend to curl due to electrostatic forces, leading to the formation of nanoscrolls, as shown in Figure 2b-c. As a result of the exfoliation, the specific surface area determined by N2-sorption isotherms increases by 2 orders of magnitude (from 2 m2 g-1 to 110 m2 g-1). Elemental analysis of the exfoliated layer shows nitrogen and carbon contents below 0.5%, indicating that the hexaniobate layers precipitated preferentially as KxH(4-x)Nb6O17. Additionally, the absence of the characteristic C-H stretching peaks at 2800–3000 cm–1 in the FTIR spectra
65
(Figure S1, supporting
information) corroborates for the conclusion that no TBA+ cations are present in the powder. X ray photoelectron spectroscopy of the as prepared material (Figure S2, supporting information) also does not show any nitrogen content in the sample surface and confirms the presence of K+ as counter ion.
10 ACS Paragon Plus Environment
Page 11 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Figure 1. X ray diffractograms of the hexaniobate before (a) and after exfoliation (b), along with the standard diffraction data (JCPDS 21-1297) for K4Nb6O17.3H2O (red).
Figure 2. SEM images of the K4Nb6O17 as synthesized (a) and after exfoliation (b). (c) TEM image of the hexaniobate nanoscrolls along with selected area diffraction pattern.
The nanoscrolls were then exposed to ethanolic solutions of the Re(I) complexes. Two different concentrations of the Re(I) complexes were employed in order to obtain different surface coverages. The same procedure was adopted for the sensitization of the TiO2 nanoparticles. The sensitized metal oxides were characterized by UV-Vis absorption spectroscopy, Figure 3. After adsorption of the complexes no changes were observed in the morphology of the nanoscrolls. Thus, despite the free energy related to the curling/uncurling of the niobate nanosheets are relatively small
64
, under our experimental
conditions, , the curled morphology is favored. 11 ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 12 of 41
Figure 3. UV-Vis spectra of bare (black) and sensitized metal oxide particles with 1 (blue) or 2 (red). (a) hexaniobate nanoscrolls (b) TiO2 nanoparticles. The dashed and solid lines indicate different surface concentrations as detailed in Table 1. Insets: molecular structure and electronic absorption spectra of 1 (blue) and 2 (red) in acetonitrile.
After adsorption of the Re(I) complexes on the surfaces of the oxides, a new absorption feature appears in the visible region that resembles the MLCT absorption bands of the respective complexes in acetonitrile solution. While for the complex 1 only a slight red-shift in the absorption maximum is observed after adsorption, for 2 the MLCT maximum shifts from 372 nm in acetonitrile to about 400 nm on the surface of the oxides. This indicates a strong interaction between the carbonyl groups in the phdo ligand and the oxide surfaces that reduces the electron density on the bipyridine rings and consequently favors the metal-to-ligand charge transfer upon excitation. The FTIR spectrum of the sensitized hexaniobate, Figure 4, confirms this strong interaction with the ketone groups in the phdo ligand. As shown in Figure 4(a) the spectrum of 2 in the 1500-2200 cm-1 region is characterized by ν(C≡O) stretching modes at 1887, 1940 and 2037 cm-1, corresponding to the A1 and the two E modes expected for the facial geometry of the complex 66-68. Moreover, a strong peak is observed at 1700 cm-1, ascribed to the ν(C=O) stretching mode of the ketone
12 ACS Paragon Plus Environment
Page 13 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
groups
69
. After adsorption, this peak can no longer be observed indicating that
the complex is anchored at the oxide surface through the carbonyl groups of the diketone. Additionally, the peaks associated with the E modes of the ν(C≡O) are slightly shifted to higher energies and become unresolved. A broad peak at 1628 cm-1 is present on the bare niobate and it is attributed to the symmetric deformation of adsorbed water molecules δs (H2O)
70
. The same trends were
also observed after adsorption on TiO2 (Figure S3 - supplementary information) suggesting that the adsorption on both oxides proceeds in a similar fashion. Similar behavior is also observed for 1, in which the intensities of the ν(C=O) peaks at 1737 and 1700 cm-1, attributed to the carbonyl groups of the carboxylates in the dcbH2 ligand, are strongly decreased after adsorption. However, these peaks can still be observed for the complex adsorbed on the niobate nanoscrolls, which may indicate that for some molecules only one of the two carboxylate groups are bonded to the niobate surface. Upon adsorption on the TiO2 nanospheres (Figure S3), these peaks disappeared completely, which suggests that both carboxylate groups are attached to the TiO2 surface. This result corroborates with those reported by Anfuso et al. for adsorption of 1 on TiO2 rutile (001) surface 31.
13 ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 14 of 41
Figure 4. FTIR spectra of 1 (blue) and 2 (red) before (a) and after (b) immobilization on the niobate nanoscrolls. The spectrum of the bare niobate (black) is shown for comparison.
The final surface coverages (mol mg-1) determined for the complexes on the two different oxides employed here are shown in Table 1. For the complex 1, the surface coverage was found to be only dependent on the initial concentration, with similar values being obtained for both, TiO2 nanospheres and niobate nanoscrolls. However, for 2, a different behavior was observed for the niobates in relation to TiO2. The surface coverage on the niobate nanoscrolls was twice as high when the initial concentration of the complex was increased, while for TiO2, a saturation limit around 3-4x10-8 mol mg-1 seems to be reached. This behavior is not related to the respective specific surface area, since the TiO2 nanoparticles employed in this study have a surface area twice as high than that of the niobate nanoscrolls (220 m2 g-1 in contrast to 110 m2 g1
). A possible reason for the better dye uptake by the niobate nanoscrolls is the
fact that the Nb5+ cations exhibit an increased charge/radius ratio as compared to Ti4+, which should result in a stronger Lewis acidity thus favoring the chelation by the dione in the phdo ligand
71
. It is worth noting here that the
14 ACS Paragon Plus Environment
Page 15 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
amount of Re(I) complexes being adsorbed through their anchor groups on the hexaniobates nanoscrolls was in the same order than the values reported for cationic metal complexes, such as [Ru(bpy)3]2+ 62 or its phosphonated derivative 72
.
Table 1. Surface coverage of 1 and 2 on hexaniobate nanoscrolls and TiO2 under different adsorption conditions Initial Surface concentration coverage Complex Substrate Sample code (µmol g-1) (µmol mg-1) 1-Nb-HC 90 0.091 KxH4-xNb6O17 1-Nb-LC 35 0.036 1 1-TiO2-HC 90 0.090 TiO2 1-TiO2-LC 35 0.038 90 0.120 2-Nb-HC KxH4-xNb6O17 35 0.051 2-Nb-LC 2 90 0.040 2-TiO2-HC TiO2 2-TiO2-LC 35 0.034 The sensitized oxides were employed as photocatalysts for CO2 reduction under experimental conditions similar to those reported by Windle et al
37
. A fixed amount of each powder was suspended in 5:1 DMF/TEOA
solutions and exposed to visible-light (λ>400 nm) irradiation under CO2 atmosphere. The possible gaseous products were analyzed by mass spectrometry with CO being the only detected photoproduct. Control experiments were carefully performed with the bare oxides or in the absence of TEOA and did not show any CO generation. Long term irradiation of the immobilized complexes in the absence of gaseous CO2 (under argon atmosphere) also did not yield in any CO, which therefore, exclude the possibility of CO photodissociation during the photolysis. These experiments show that the CO detected during the photocatalytic experiment comes from the reduction of the gaseous CO2 by the Re(I)-based catalysts in the presence of
15 ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
TEOA, that act as sacrificial agent as previously reported
Page 16 of 41
73, 74
. The turnover
numbers (TONCO), defined as the number of molecules of CO formed per molecule of the Re(I) catalyst, were determined for each sample after 20 h irradiation and are listed in the Table 2. As two different surface coverages were tested for each photocatalyst, the powders are referred to LC and HC for low and high surface concentrations, respectively, as specified in Table 1. For clarity, the total number of mols of the respective Re(I) complex in the reactor is shown in Table 2. Figure 5 exemplifies the mass spectra of the reactor atmosphere having 1 immobilized on niobate nanoscrolls in DMF/TEOA before and after irradiation. It is possible to clearly observe the increase in the m/z = 28 peak after irradiation, which is attributed to photorreduction of CO2 into CO by the Re(I) complex adsorbed on the niobate nanoscrolls.
Figure 5. Mass spectra of the photoreactor atmosphere before (black) and after (blue) 20 h of irradiation. The reactor (50 mL) was filled with 25 mL of DMF/TEOA (4:1) solution having 28 mg of niobate nanoscrolls sensitized by 1. Argon is used as carrier gas.
16 ACS Paragon Plus Environment
Page 17 of 41 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Table 2. Turnover number for photoreduction of CO2 to CO employing the bare or the immobilized Re(I) complexes. TONCO after 20 h µmols of Re(I) Photocatalyst TOF (h-1) irradiation catalyst 1 2.8 0.7 9±4 2 3.0