Han
Zhou
ab,
Peng
Li
ac,
Jianjun
Guo
ac,
Runyu
Yan
b,
Tongxiang
Fan
b,
Di
Zhang
b and
Jinhua
Ye
*acd
aInternational Center for Materials Nanoarchitectonics (WPI-MANA) and Environmental Remediation Materials Unit, National Institute for Materials Science (NIMS), 1-1, Namiki, Tsukuba, Ibaraki 305-0044, Japan. E-mail: Jinhua.YE@nims.go.jp
bState Key Lab of Metal Matrix Composites, Shanghai Jiaotong University, Shanghai, 200240, China
cGraduate School of Chemical Sciences and Engineering, Hokkaido University, Sapporo, Japan
dTU–NIMS Joint Research Center, School of Materials Science and Engineering, Tianjin University, 92 Weijin Road, Nankai District, Tianjin 300072, P. R. China
First published on 16th September 2014
Artificial photosynthesis, the photochemical fixation and recycling of CO2 back to hydrocarbon fuels using sunlight and water, is both a significant challenge and an opportunity that, if realized, could have a revolutionary impact on our energy system. Herein, we demonstrate one of the first examples using biomass derived hierarchical porous photocatalysts for CO2 photo-fixation into sustainable hydrocarbon fuels. A generic method is proposed to build a series of alkaline tantalates MTaO3 (M = Li, Na, K) with hierarchical anatomy from macro- to nanoscales using activated carbonized tree trunks as templates. Artificial photosynthesis is carried out on MTaO3 series using only artificial sunlight, water, and carbon dioxide as inputs to produce carbon monoxide and methane as the main outputs. The CO2 photo-fixation performance can be enhanced by introducing a macropore network, which mainly enhances light transfer and accelerates gas diffusion. The research provides prototype models that integrate individual nanoscale components into higher level macroscopic artificial photosynthetic systems for better solar-to-fuel conversion efficiencies. This work would have potential significance for the ultimate construction of “artificial trees” and provide envisions creating “forests” of these CO2-capturing artificial trees to remove carbon dioxide from the atmosphere and convert it into sustainable fuels.
Morphology control strategy has been an effective and versatile approach for promoting CO2 photo-fixation activities,20 involving the construction of nanostructures,10,21,22 micro/mesoporous structures,11,12 hollow structures,23–25 metal–organic frameworks (MOFs)26 with highly porous cavities, etc. In recent years, materials with hierarchical porous anatomy have been extensively researched and are widely used in catalysis.27–29 This is because materials with hierarchical porosity can provide macro to nanolength sizes of pores for reaction, interfacial transport, or dispersion of active sites and reduce diffusion paths or reduce diffusion.27,28 However, to date there are only few reports on the oriented design, controlled synthesis and ultimate application of hierarchically porous materials for CO2 photo-fixation. Furthermore, the general synthesis of alkaline tantalates with a well-defined hierarchical porous anatomy has not been reported yet.
In green plants, leaves are well-known as the main photosynthetic organs. Tree trunks, a main part of trees, function as water/mineral transportation pathways for the photosynthesis of leaves. They exhibit a hierarchically built anatomy which act as the central “plumbing system” in a tree, forming a network of tubes as transportation paths with three-dimensional (3D), highly hierarchical, porosity and high system connectivity that carries water and minerals up from the roots to the leaves, and sugar from the leaves down to the branches, trunk, and roots. The most distinct morphological feature of tree trunks is the open porous system of the tracheidal cells, which provide the transportation path for water in the living wood and yields an uniaxial pore structure with anisotropic mechanical properties.30 Furthermore, tree trunks have a rather high surface area of up to hundreds m2 g−1. Thus, such a hierarchical anatomy would be a potential candidate for the directed synthesis of hierarchical systems.
Herein, we demonstrate one of the first examples using biomass derived hierarchical porous catalysts for CO2 photo-fixation into sustainable hydrocarbon fuels. A generic method is proposed to build a series of alkaline tantalates MTaO3 (M = Li, Na, K) with hierarchical anatomy using activated carbonized tree trunks as templates. Artificial photosynthesis is carried out on MTaO3 series using only artificial sunlight, water, and carbon dioxide as inputs to produce carbon monoxide and methane as the main outputs. The CO2 photo-fixation performance can be enhanced by introducing a macropore network because of the enhanced light transfer and faster gas diffusion in hierarchical meso/macroporous systems. The research provides prototype models to integrate individual functional components into higher level macroscopic artificial photosynthetic systems for better solar-to-fuel conversion efficiencies. This work would have potential significance for ultimate construction toward “artificial trees” or “artificial plants” and one could envision creating “forests” of these CO2-capturing artificial trees to remove carbon dioxide from the atmosphere and convert it into sustainable fuels.
In this work, a typical coniferous wood White pine was chosen as a template. As shown in Fig. 2a and 2b, white pine has a nearly monomodal microsized pore distribution. The mean pore diameter of the tracheids is 10 μm. The longitudinal section is composed of oriented long microtubes with a diameter of 10 μm (Fig. 2c and 2d). Cells arranged in a radial direction (rays) and pores in the cell walls create a 3D macropore network for transportation. Furthermore, cell walls are composed of numerous micropores according to the N2 adsorption measurement (Fig. 3a), which are from the nanosized molecular fibers. Such hierarchical porous anatomy endows the wood a high surface area of up to 345 m2 g−1 (Fig. 3a). Here, an activation process was applied on the carbonized wood template to significantly increase its surface area, approaching ∼1757 m2 g−1 (Fig. 1e and 3a). An activation process causes more micropores to form and thereby causing a major relative increase in pore volume in the micropore range (Fig. 3a). Obviously, main micropores are formed during partial oxidation and removal of carbon in hot air, which leads to the increase in specific surface area and porosity. Activated carbonized wood with 3D hierarchical micro/meso/macroporous anatomy and high surface area was a promising template for the synthesis of the corresponding alkaline tantalates replica. Under vacuum infiltration conditions, it was easier for the precursor solution to infiltrate into the micro/mesopores of the carbonized samples. Because there are functional groups on the surfaces of the carbonized samples, the precursors could interact with the surfaces, which facilitated targeted materials assembly. The major biopolymeric constituents in wood are cellulose, hemicellulose, and lignin with some additional macromolecular compounds, such as different kinds of fat, oil, wax, minerals, alcaloides, etc., as minor constituents.31 According to TGA data (ESI, Fig. S3a†), the organics could be decomposed completely at around 450 °C. Hence, after calcination at 550 °C in O2 atmosphere for 10 h, the organics would be removed completely (ESI, Fig. S2†) leaving crystalline tantalates MTaO3 (M = Li, Na, K), as demonstrated by XRD (Fig. 3b). FESEM and TEM images show the hierarchical porous anatomy of the products. Considering NaTaO3 as an example, the product has a very loose feature (ESI, Fig. S4†). It can be observed from the cross-section that the products have highly porous structures with pores in the range of several micrometers (Fig. 2e). Longitudinally, it has tube-like structures (Fig. 2f). A TEM image (inset of Fig. 2e) shows that the macropore networks are composed of mesoporous nanocrystalline building blocks.
In general, CO2 in the presence of water vapor can be photoreduced to hydrocarbon fuels using a wide-band-gap semiconductor as a photocatalyst.32 Because of the irradiation of full arc Xe lamp, the existing form of water for the reaction is vapor. Theoretically, alcohol or methanol could serve as electron donors to increase the activities. However, because of the well-known process of photocatalytic reforming of ethanol, in the presence of alcohol the production of CO and CH4 could increase significantly, which is derived from the photocatalytic reforming of ethanol. Thus, it is not easy to analyze the carbon sources of CO and CH4. According to the diffuse reflection spectra of alkali tantalates (Fig. 3c), the onsets of the absorption of LiTaO3, NaTaO3 and KTaO3 were 256, 310 and 344 nm, respectively. Thus, the band gaps of LiTaO3, NaTaO3 and KTaO3 were estimated to be 4.8, 4.0 and 3.6 eV, respectively. Here, we performed artificial photosynthesis of CO2 + gaseous H2O reaction in a gas–solid system over the MTaO3 series. Considering NaTaO3 as an example, bare NaTaO3 evolves CO and CH4 as the main products in the absence of any sacrificial agents (Fig. 4a and 4b). It is well-known that CO2 photoreduction mainly undergoes two courses, including oxidation and reduction processes. In the oxidation process, the photogenerated holes in the valence band oxidize water to generate hydrogen ions via the half-reaction (2H2O + 4h+ → O2 + 4H+). In the reduction course, there is a chain reaction to reduce CO2 to CH4 (CO2 + 2H+ + 2e− → CO + H2O, CO2 + 4H+ + 4e− → HCHO + H2O, CO2 + 6H+ + 6e− → CH3OH + H2O, CO2 + 8H+ + 8e− → CH4 + 2H2O).32 The edges of the valence band (EVB) and conduction band (ECB) of NaTaO3 are determined to be 2.993 and −1.007 V (vs. normal hydrogen electrode, NHE) via the Mulliken electronegativity method, respectively.33EVB of NaTaO3 is more positive than that of E°(H2O/H+) (H2O → 1/2O2 + 2H+ + 2e−, E° redox = 0.82 V vs. NHE), and ECB is more negative than that of E° (CO2/CO) (CO2 + 2e− + 2H+ → CO + H2O, E° redox = −0.53 V vs. NHE) and E° (CO2/CH4) (CO2 + 8e− + 8H+ → CH4 + 2H2O, E° redox = −0.24 V vs. NHE). This indicates that the photogenerated electrons and holes on the irradiated NaTaO3 can react with the adsorbed CO2 and H2O to produce CO and CH4. Other products, such as HCOOH, HCHO, CH3OH, were not detected probably because of the gas-phase CO2 photoreduction with low proton concentrations; CO is the primary first step product instead of HCOOH.34–36 The intermediates produced during the reduction tend to favor the formation of CH4 instead of CH3OH, HCHO and HCOOH.34–36 Furthermore, the strong oxidation power of photogenerated holes (or OH radicals) that can react with intermediates and products of CO2 conversion in reactions34–36 make the net yield negligible. It is also worth mentioning that in our semiconductor systems, H2 was not detected probably because in the absence of sacrificial agents in our system, the produced H2 served as reductant for CO2 photoreduction.
Hierarchical porous anatomy could influence their activity. Considering NaTaO3 as an example, activated carbonized wood-templated NaTaO3 exhibits about a 2.23-fold improvement in activities than non-templated NaTaO3 based on the same amount (Fig. 4a) mainly due to enhanced light transfer and faster gas diffusion. Hendricks and Howell37 indicated that the porous structure of ceramics creates complex electromagnetic scattering and interference patterns within the structure. Particularly, when the size of the voids is comparable to the wavelength of the incident light, Mie's scattering occurs, in which light scatters strongly along the forward direction. This scattering produces a pattern similar to an antenna lobe with a sharper and more intense forward lobe (Fig. 4a, right part).38 According to the diffuse reflection spectra and the spectrum of Hg–Xe lamp (ESI, Fig. S5†), the effective incident light wavelength is between 200–310 nm. According to the mercury porosimeter (Fig. 3d), the quantity of macropores around 200–310 nm comparable with the incident light wavelength in wood-templated NaTaO3 are obviously much more than that of the non-templated NaTaO3. Therefore, the path length of the incident light increases,39 leading to an enhanced light utilization efficiency. The scattered light then transfers to and is absorbed by the neighboring pores, thus inducing more photo-excited electrons for the reduction (Fig. 4a, right part).
On the other hand, gas diffusivity is another key factor. When the diameter of the pore is considerably greater than the mean free path of the gas molecules, the diffusing molecules interact with each other more than with the pore walls, thereby minimizing the wall effects on transport.40 In our case, the mean free paths of CO2, CH4, CO and H2O were calculated to be about 74, 70, 72 and 139 nm according to eqn (1), respectively. Where K is 1.38 × 10−23, T is assumed to be 323 K in our experiment and D0 refers to the diameter of gas molecules (nm).
(1) |
According to the SEM and mercury porosimeter, a number of macropores are in the range of several to hundreds of micrometers, and thus the pore diffusivity is essentially the same as the molecular diffusivity, in which the diffusion coefficient is considerably larger than that in mesopores (Fig. 4a, right part). In contrast, gas diffusion in non-templated system with much fewer and smaller pores is mainly Knudsen diffusion, where the gas molecules frequently collide with the pore walls (Fig. 4a, right part). Thus, the gas diffusion rate is smaller and a longer time is required for reactants to move into the deeper layers as well as for products to move from the deeper layers into the atmosphere. The higher activity of the activated carbonized wood-templated system (Fig. 4a, 1#) than the carbonized wood-templated system (Fig. 4a, 2#) is mainly because of higher surface areas and higher volume of mesopores derived from the porous activated carbon templates, (ESI, Table S1†) and provide more reaction sites, thus enhancing the overall performance.
The evolution rates of CO and CH4 over NaTaO3 could be significantly enhanced by a factor of 3.1 and 8.4, respectively, after loading Au cocatalyst to facilitate the proton-coupled multielectron transfer (Fig. 4b). A precipitation method was used for the deposition of Au nanoparticles. XPS spectrum (ESI, Fig. S6†) demonstrates the formation of metallic Au. The size of Au is only about 3 nm (ESI, Fig. S7†) with good homogeneity, which coincides with a literature report.41 After loading with about 1 wt% Au onto MTaO3 series, the activities were in the order of LiTaO3 > NaTaO3 > KTaO3, as compared in Fig. 4c. According to the Mulliken electronegativity method,33 the edges of the conduction band of LiTaO3, NaTaO3, KTaO3 were estimated to be −1.302 V, −1.007 V and −0.98 V (vs. NHE), respectively (inset of Fig. 4c). The order of the photocatalytic activities was consistent with that of the conduction band levels, indicating that wide band gap semiconductors with higher reduction potentials are more favorable for CO2 photo-fixation. We compared our results with other photocatalytic systems with respect to efficiency and selectivity, and the data is shown in Table 1. However, because the experimental conditions (light intensity, irradiation distance, catalysts amount, and others) are different, it may not be suitable comparison. Here, we also compared our photocatalytic systems with some typical semiconductors (published by our group) measured with the same reactor system (Table S2†).
Light source | Catalyst | Co-catalyst | Reaction medium | Products | SelCH4a/% | Ref. |
---|---|---|---|---|---|---|
a SelCH4/% = mol (CH4)/mol (CH4 + CO). | ||||||
300 W Xe lamp | Leaf-architectured SrTiO3 | 1 wt% Au | CO2 and H2O vapor | CO (350 nmol h−1 g−1) | 44.1 | 46 |
CH4 (275 nmol h−1 g−1) | ||||||
UV Xe lamp | TiO2 rods with {010} facets | 1 wt% Pt | CO2 and H2O vapor | CH4 (5.7 nmol h−1 g−1) | 100 | 47 |
300 W Xe lamp UV | hollow anatase TiO2 single crystals with {101} facets | 1 wt% RuO2 | CO2 and H2O vapor | CH4 (1.725 nmol h−1 g−1) | 100 | 48 |
350 W Xe lamp UV | SiO2-Pillared HNb3O8 | 0.4 wt% Pt | CO2 and H2O vapor | CH4 (2.9 nmol h−1 g−1) | 100 | 49 |
300 W Xe arc lamp visible light λ > 420 nm | Na2V6O16 nanoribbons | 1 wt% Pt and 1 wt% RuO2 | CO2 and H2O vapor | CH4 (190 nmol h−1 g−1) | 100 | 50 |
Xe arc lamp visible light λ > 420 nm | W18O49 nanowires | — | CO2 and H2O vapor | CH4 (666 ppm h−1 g−1) | 100 | 21 |
visible light λ > 420 nm | ZnAl2O4-modified mesoporous ZnGaNO | 0.5 wt% Pt | CO2 and H2O vapor | CH4 (9.2 nmol h−1 g−1) | 100 | 51 |
Xe lamp UV | Zn2GeO4 nanobelts | 1 wt% Pt and 1 wt% RuO2 | CO2 and H2O vapor | CH4 (25 nmol h−1 g−1) | 100 | 10 |
300 W Xe arc lamp visible light λ > 420 nm | sheaf-like, hyperbranched Zn1.7GeN1.8O | 1 wt% Pt and 1 wt% RuO2 | CO2 and H2O vapor | CH4 (9 nmol h−1 g−1) | 100 | 52 |
200 W Hg-Xe arc lamp | NaTaO3 | 1 wt% Au | CO2 and H2O vapor | CO (173 nmol h−1 g−1) | 17.3 | This work |
CH4 (36 nmol h−1 g−1) |
For all the samples, oxygen is not detected. Water oxidation is much more difficult kinetically and energetically than H2 evolution, requiring a large overpotential. Oxygen generated by water oxidation is partially used for the oxidation of the evolved products (HCOOH, HCHO, CO, etc.)42 On the other hand, O2 evolution is controlled by the interfacial reaction such that the semiconductor should provide a favorable reaction site for the O2 formation process. Otherwise, O2 can be absorbed on surface oxygen vacancies43 and undesirably absorbs electrons to form O2− or other species, such as H2O2, that chemisorbs on the surfaces of catalysts and can increase the redox energy of the half-reaction, making the necessary overvoltage still larger,44 thereby further inhibiting O2 production. We checked the XRD patterns before and after irradiation on wood-templated NaTaO3 (Fig. S8†) to test the chemical stability. Furthermore, Fig. 4b and 4c show that after long term irradiation (24 h–54 h), the activities of MTaO3 (M = Li, Na, K) series remained almost linear, which further demonstrates the stability of these catalysts. Finally, to confirm that the hydrocarbon fuels were generated from the reduction of CO2via the protons released from H2O oxidization and photogenerated electrons, control experiments were carried out, as shown in Fig. 4d. When the experiment was carried out in the absence of H2O, catalyst or light irradiation, very little CH4 was detected due to only 1 ppm of CH4 contamination from air during samples. When the CO2 gas was replaced by Ar gas, a small amount of CH4 was found which should be generated from the photoreduction of the remaining CO2 on the sample surface.45
Footnote |
† Electronic supplementary information (ESI) available: FESEM images, TGA curves, XPS spectrum, TEM image, the spectrum of the lamp, reaction setup. See DOI: 10.1039/c4nr03019b |
This journal is © The Royal Society of Chemistry 2015 |