Next Article in Journal
Layup Configuration Effect on Notch Residual Strength in Composite Laminates
Next Article in Special Issue
Core Level Spectra of Organic Molecules Adsorbed on Graphene
Previous Article in Journal
A Dislocation-Scale Characterization of the Evolution of Deformation Microstructures around Nanoindentation Imprints in a TiAl Alloy
Previous Article in Special Issue
Improved Photo-Ignition of Carbon Nanotubes/Ferrocene Using a Lipophilic Porphyrin under White Power LED Irradiation
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:

TiO2@PEI-Grafted-MWCNTs Hybrids Nanocomposites Catalysts for CO2 Photoreduction

ICCOM-CNR (Istituto di Chimica dei Composti OrganoMetallici-Consiglio Nazionale delle Ricerche), SS Bari, Via Orabona 4, 70126 Bari, Italy
Dipartimento di Chimica, Università di Bari “A. Moro”, Via Orabona 4, 70126 Bari, Italy
IPCF-CNR (Istituto per i Processi Chimico Fisici–Consiglio Nazionale delle Ricerche), SS Bari, Via Orabona 4, 70126 Bari, Italy
CNR-IC (Consiglio Nazionale delle Ricerche–Istituto di Cristallografia), Via Amendola 122/O, 70126 Bari, Italy
Authors to whom correspondence should be addressed.
Materials 2018, 11(2), 307;
Received: 19 January 2018 / Revised: 13 February 2018 / Accepted: 13 February 2018 / Published: 20 February 2018
(This article belongs to the Special Issue Hard and Soft Hybrid Functional Materials)


Anatase (TiO2) and multiwalled carbon nanotubes bearing polyethylenimine (PEI) anchored on their surface were hybridized in different proportions according to a sol-gel method. The resulting nanocomposites (TiO2@PEI-MWCNTs), characterized by BET, XRD, XPS, SEM, and UV techniques, were found efficient catalysts for CO2 photoreduction into formic and acetic acids in water suspension and under visible light irradiation. PEI-grafted nanotubes co-catalysts are believed to act as CO2 activators by forming a carbamate intermediate allowing to accomplish the first example in the literature of polyamines/nanotubes/TiO2 mediated CO2 photoreduction to carboxylic acids.

1. Introduction

During the past decade, great deal of attention has been dedicated to converting solar energy into chemical energy in the form of so-called “solar fuels”, such as H2, methanol, methane, formic acid, etc. In this context, the reduction of carbon dioxide is gaining more and more importance in the research area of chemistry and materials, not only for solving the problems resulting from environmental pollution, but also for finding ways to maintain the carbon resources which are being depleted by the burning of fossil fuels [1].
A very promising method is the photoreduction of CO2 to produce clean hydrocarbon fuels under sunlight irradiation, a process that mimics the natural photosynthesis in plants. Among all photocatalysts, anatase TiO2 still remains the most promising candidate considering its photostability, corrosion resistance, low cost, and strong oxidation power [2,3,4].
However, photocatalytic efficiency of TiO2 is limited due to its large band gap (3.2 eV), which can only be excited under ultraviolet irradiation and rapid recombination of photoinduced electrons and holes. To solve these problems, a variety of dopants has been investigated, ranging from transition metals (e.g., Pd, Pt, Fe, etc.) [5,6,7,8,9,10] and their oxides (e.g., Cu2O, CeO2, etc.), [11] to non-metal ions (N and I) [12] and rare hearth derivatives (La2O2) [13].
During the past decade, there has been a growing interest in hybridizing TiO2 with carbon nanostructured materials, such as nanotubes (CNTs) [14,15,16,17,18] and graphene [19], that play the role of transferring photogenerated electrons from the TiO2, suppressing the recombination rate of the electron–hole pairs. Recently, a new strategy is emerging concerning the modification of TiO2 with co-catalysts capable of enhancing CO2 adsorption [20]. Main approaches are based on metal oxides (mainly MgO) [21,22], metal organic framework (MOFs) [23] and amines [24,25].
In this context, being carbon nanotubes amongst the most promising solid sorbents for CO2 capture [26,27], in particular when their walls are decorated with CO2-philic groups [28,29,30,31,32], we sought to enhance photocatalytic performance of titania by means of its conjugation with carbon nanotubes bearing polyamines anchored on their surface, with the specific task of adsorbing the CO2 reactant and help the redox process.
With this in mind, in our ongoing efforts aimed at searching new green catalytic methods [33,34,35,36,37,38], we prepared a series of hybridized materials based on anatase and amine-grafted multiwalled carbon nanotubes (TiO2@amine-MWCNTs) and tested their ability to serve as an efficient catalyst for photoreduction of carbon dioxide.

2. Materials and Methods

2.1. Chemicals

Common commercial solvents and reagents of high purity were employed. Commercial Caroat® (Pullach, Germany) triple salt (2KHSO5·KHSO4·K2SO4), a gift from Peroxid-Chemie (Degussa, Germany), was the source of potassium monoperoxysulfate (caroate) for the synthesis of TFDO [39,40]. MWCNTs (purity >90 wt.%, diameter between 0.7 and 1.4 nm) are commercially available from Sigma-Aldrich (Milan, Italy) in form of powder.
Carbon dioxide, O2, Argon and Helium were with purity of 99.99%, a gas burette (Figure S1) was used to measure gas volume in adsorption/desorption experiments. Formic and acetic acid analyses were performed with an Ion Chromatograph Dionex DX120 (Ion Pac ICE-AS6 Analytical Column, Monza, Italy); 0.8 mM heptafluorobutyric acid (Sigma-Aldrich) was used as eluent (flow 1.00 mL/min) and 5.0 mM tetrabutylammonium hydrate (Sigma-Aldrich) as regenerating eluent (flow 4.5 mL/min).
Formic acid 99% and acetic acid (Sigma Aldrich) were employed as standard for building IC calibration curves. Analyses were carried out by using a sample loop of 25 μL, with a column pressure less than 640 PSI and a background of 35–40 μS.
GC analyses for liquid and gas phase were performed with a GC Tracera Shimadzu 2010 (Milan, Italy) with a Detector BID-2010 (Shimadzu, Milan, Italy) plus and a Micropacked ST column (temperature program isotherm at 40 °C 30 min). Infrared analyses were performed in the range 400–4000 cm−1 (64 scans), using a PerkinElmer 2000 FT-IR spectrometer (Milan, Italy).

2.2. Physico-Chemical and Morphological Characterization of Nanocomposites

Thermogravimetric analyses were recorded on a TGA Q500 (TA Instruments, New Castle, GA, USA) using a flowing nitrogen atmosphere. The samples (about 1 mg per sample) were equilibrated at 100 °C for 20 min and then heated at a rate of 10 °C min−1 up to 800 °C.
Elemental analyses were performed on a Thermo Flash EA 1112 series CHNS-O elemental analyzer (Monza, Italy) with an accepted tolerance of 0.4 units.
TEM (Transmission electron microscopy) analyses were performed with a TEM Philips EM208 instrument (Vienna, Austria) using an accelerating voltage of 100 kV. The samples were prepared by dropping aliquots of the DMF dispersions onto TEM grids (200 mesh, Nichel, carbon only, Ted Pella, Milan, Italy).
BET (Brunauer-Emmett-Teller) specific surface area was obtained by N2 adsorption-desorption method on powder samples using a Micromeritics TriStar II 3020 (Micromeritics, Norcross, U.S.A.). The samples (500 mg) were pre-treated at 80 °C for 2 h before N2 adsorption.
FE-SEM investigations were performed by a Zeiss Sigma (Milan, Italy) microscope operating in the range 0.5–20 kV and equipped with an in-lens secondary electron detector. FE-SEM samples were prepared by sticking the powder on double sided carbon tape. Samples were mounted onto stainless-steel sample holders by using and grounded by silver paste.
UV-Vis diffuse reflectance spectra were recorded with a UV-vis-NIR Cary 5 (Varian, Palo Alto, CA, USA) spectrophotometer equipped with an integrating sphere (BaSO4).
X-Ray powder diffraction data were collected at room temperature by using an automated Rigaku RINT2500 laboratory diffractometer (50 KV, 200 mA, Neu-Isenburg, Germany) equipped with the silicon strip Rigaku D/teX Ultra detector. Detailed XRD analyses of hybrids nanocomposites are showed in Figure S2.
X-ray photoelectron spectroscopy (XPS) analyses were performed on a PHI VersaProbe II spectrometer (Phisical Electronics, Kanagawa, Japan) equipped with a monochromatic Al Kα X-ray source (1486.6 eV) operating at a spot size of 100 μm, corresponding to a power of 24.4 W. Survey (0–1400 eV) and high resolution (C 1s, O 1s, N 1s, Ti 2p, Cl 2p, F 1s) spectra were recorded in FAT (fixed analyzer transmission) mode at pass energy of 117.4 eV and 46.95 eV, respectively. All spectra were acquired at a take-off angle of 45° with respect to the sample normal. Dual-beam charge neutralization was constantly applied during analysis. Charge correction of the spectra was performed by taking the sp2 graphitic component of the C 1s spectrum as internal reference (binding energy, BE = 284.6 eV).
XPS analysis was repeated on three different spots for each sample. During analyses, special care was devoted to verifying that no change in the samples was induced by exposure to the X-ray beam and the charge neutralization dual-beam. Detailed spectra processing was performed by commercial MultiPak software (Version, 30-10-2013, Ulvac-PHI, Inc., Kanagawa, Japan). The high-resolution spectra were fitted with mixed Gaussian-Lorentzian peaks after a Shirley background subtraction.
The DO 9721 quantum photo-radiometer (Delta Ohm, Pordenone, Italy) and thermometer data logger were used for measuring illuminance, irradiance, luminance and temperature.

2.3. Preparation of ox-MWCNTs (2) with TFDO

Preparation was accomplished according to our previous method [41,42]. MWCNTs (600–1000 mg) were placed in CH2Cl2 (50–100 mL) and the mixture was sonicated for 30 min. An aliquot (35 mmol) of the standardized cold solution of methyl(trifluoromethyl)dioxirane (TFDO, 70 mL, 0.5 M) in 1,1,1-trifluoropropanone (TFP), was then added in one portion to the mixture, which was stirred and kept at 0 °C. After 24 h the reaction was complete, the mixture was filtered, and ox-CNTs 2 were washed several times with CH2Cl2 followed by MeOH, with recovery of 700–1300 mg.

2.4. Epoxide Ring Opening of ox-MWCNTs (2): Preparation of Amine-Grafted-MWCNTs 3 and 4

This procedure was used for preparation of amine grafted-MWCNTs 3 and 4 [41,42]. Oxidized nanotubes 2 (1 g) were dispersed in 1,6-hexamethylenediamine (3.7 g) or branched polyethylenimine (5 g PEI MW 600, 99% of purity) and the mixture was heated at reflux at 140 °C under N2 for 12 h. Next, the reaction mixture was diluted with methanol (20 mL) and filtered through a PTFE membrane filter paper (0.2 μm). The solid was washed several times with CH2Cl2 followed by MeOH to remove any excess of amine leading to HMDA-MWCNTs (3, 1.20 g) or PEI -MWCNTs (4, 1.25 g). Elemental analyses for 3: C (95.45%), H (3.24%), O (0.30%), N (1.01%); for 4: C (91.59%), H (5.61%), O (0.17%), N (2.63%).

2.5. Preparation of hybrids nanocomposites photocatalysts 1A, 1C, 4A-C

Preparation of hybrids nanocomposites was accomplished to previous method [14], titanium tetrachloride (98% TiCl4), hydrochloric acid (38% HCl) and distilled water with a molar ratio of TiCl4:HCl:H2O = 0.1:1:200 were homogenized under magnetic stirring for 30 min. The thus obtained transparent mother solution was then used as the raw material for preparing nanocomposites for photocatalytic experiments. Proper amounts of both p-MWCNTs (1) and functionalized PEI-MWCNTs (4) were separately dispersed into the proper volume of mother solution according to Table 1.
After suspension, mixture was sonicated and then ammonia was slowly added (until neutrality) under vigorous stirring, thus inducing TiO2 precipitation and formation of random agglomerates by inclusion of CNTs [14]. After filtration, nanocomposites 1A, 1C and 4A-C were washed with distilled water and dried at 80 °C for 24 h.

2.6. Photocatalytic Experiments

The photocatalytic activities of samples 1A-C, 4A-C were evaluated by the reduction of CO2 in H2O [9,43] (see Section 3.3). The apparatus used for the photocatalytic experiments consists of a three necked Pyrex batch photoreactor of cylindrical shape containing 20 mL of aqueous suspension. The photoreactor was provided with a jacket for cooling water circulation and ports in its upper section for the inlet and outlet of gases, for sampling and for pH and temperature measurements. A HRC UV-VIS lamp 300 W (Sanolux, Milan, Italy) and Xe-Halogen lamp 400 W (Radium, Milan, Italy) were placed in proximity (5–6 cm) of the reactor. Argon was bubbled for 30 min, to avoid the presence of air, and then CO2 for approximately 60 min before switching on the lamps. The amounts of catalyst used were 150 and 500 mg in 20 mL of solution (loading of 7.5 and 25 mg/mL). The initial pH was 4.58. The temperature inside the reactor was held at approximately 25 °C by a continuous circulation of water in the jacket around the photoreactor. The photoreactivity runs lasted in 5.0 h and the products were detected by Ion Cromatography and GC-BID.

2.7. UBA Reduction Experiments

Experiments were performed following a protocol previously reported in literature [18,44,45]. The proper amount of the TiO2/MWCNTs powder was dispersed in a mixture of chloroform (61%) hexane (27%) and ethanol (12%), obtaining a concentration of 5000 ppm. Finally, the required volume of a stock solution of UBA in EtOH (2.5 × 10−3 M) was added to reach the desired CHCl3:Hexane: EtOH ratio, and fix the final UBA concentration at 10−5 M. Such a reaction mixture was poured in a quartz cuvette, sealed by a Teflon-faced rubber cap and purged under N2 flow for 20 min, under stirring. Such a procedure has a twofold role: (i) to remove oxygen from the reaction environment and (ii) to promote the absorption-desorption equilibria between the photocatalyst and the UBA. Next, the mixture, was irradiated under continuous stirring with UV light using a medium pressure 200 W mercury lamp (λ > 250 nm), equipped with neutral density filters in order to achieve a light flux of 5 mW/cm2. At scheduled time intervals, the cuvette was removed from the light source and the reaction mixture was transferred in a centrifuge tube under inert atmosphere. The UBA/photocatalyst suspension was separated by centrifugation, and the liquid phase analyzed by absorption spectroscopy. The reaction was monitored by recording difference absorption spectra of the irradiated reaction mixtures. Any change in the absorption line-shape was then clearly identified for each sample, by considering as reference the respective unphotolyzed solution.

3. Results and Discussion

3.1. Synthesis and Characterization of Amine-Grafted-MWCNTs

Grafting of amines onto the carbon nanotubes were performed with a recent approach based on epoxidation of CNTs followed by nucleophilic oxirane ring opening [41,42]. This strategy is a greener alternative to the most used method via chemical oxidation with strong acids (H2SO4/HNO3), that tends to damage the graphite-like structure of nanotubes [31,46].
The milder functionalization was accomplished by treatment of pristine nanotubes 1 (p-MWCNTs) with methyl (trifluoromethyl) dioxirane (TFDO), a well-known oxidant suitable for efficient and selective epoxidations of alkenes under mild and neutral conditions. Next, epoxidized nanotubes 2 (ox-MWCNTs) were subjected to the oxirane ring opening reaction with two different polyamines, namely 1,6-hexamethylendiamine (HMDA) and branched polyethylenimine (PEI), affording the corresponding amine-grafted MWCNTs 3-4 (Figure 1).
Evidences for the CNTs functionalization were provided by FT-IR. Epoxide ring-opening and post-functionalization of grafted nanotubes PEI-MWCNTs (4) were spectroscopically confirmed by NH2 band appeared at 3400 and 3350 cm−1, due to the NH2 symmetric stretch. Further evidence was given by signals at 1461 and 1380 cm−1, due to the bending of CH2 groups, while bands at 1068 and 1050 cm−1 were attributed to C–N and C–O bending (Figure 2).
TGA analyses (Figure 3a) of amine-grafted nanotubes 3 and 4 revealed similar weight loss percentages of 14.4% and 14.0%, respectively, thus indicating a quite similar amine loading on the nanotubes surface. As control experiments, both p-MWCNTs 1 and grafted PEI-MWCNTs 4’ obtained after an adsorption/desorption cycle (namely des-PEI-MWCNTs) were subjected to the same analysis.
The weight loss of 12.3% for desorbed PEI-MWCNTs (4’) accounted for a substantial stability of grafted amines-CNTs under the CO2 capture conditions. Moreover, comparison of TEM images of PEI-MWCNTs 4 (Figure 3b) and p-MWCNTs 1 (Figure 3c) revealed no substantial change in morphology upon surface functionalization of p-MWCNTs.
Loading of CO2-philic amine groups of modified MWCNTs 3-4 was evaluated by means of total N-content (%), whereas their sorbent capacity was estimated in a series of adsorption/desorption experiments and compared with that of pristine p-MWCNTs (1) (Table 2). As expected, grafting of amine moieties onto the surface of MWCNTs increased their sorbent capacity by conjugating physical adsorption of nanotubes and chemical absorption of CO2-philic functionalities. Additionally, results in Table 2 confirmed that the CO2 capture process proved to be perfectly reversible for amine-grafted-MWCNTs 3-4, for which CO2 could be quantitatively released at 80 °C.
On these bases, also taking into account the recent literature [47] highligting polyethylenimine as one of the greatest candidates for CO2 sequestration processes, PEI-grafted MWCNTs 4 showing the best capture performance was selected as co-catalysts of titania in the CO2 photoreduction.

3.2. Preparation and Characterization of Hybrid Nanocomposites Photocatalysts

Hybrid nanocomposites photocatalysts were prepared according to a sol-gel method [14]. At this end, functionalized nanotubes 4 were suspended in a aqueous HCl solution of TiCl4 from which TiO2 was precipitated by addition of ammonia, thus forming random agglomerates by inclusion of CNTs (Scheme 1) [13]. The ensuing TiO2@PEI-MWCNTs composites were collected by filtration, washed with distilled H2O and dried at 80 °C for 24 h. For the photocatalytic experiments, a number of hybrid nanocomposites were selected (1A, 1C, 4A-C) using different amounts of pristine nanotubes 1 and PEI-modified- MWCNTs 4, as listed in Table 3.
Hybridized materials were characterized by BET, XRD, XPS, FE-SEM, and UV techniques (see Supplementary Materials for details). BET analyses displayed an expected trend in which the presence of carbon nanotubes remarkably increased the surface area of composites with respect to titania (Table 3).
XRD spectra were reported in Figure 4. The diffraction pattern of PEI-grafted MWCNTs 4 showed a very low degree of crystallinity (Figure 4a). The diffraction patterns of the two hybrid composites 1A and 4A, consisting of TiO2 with minimal amounts (2%) of carbon nanotubes, exhibited similar features of anatase phase (Figure 4b). As expected, on increasing the PEI-MWCNTs content up to 10% (composite 4B), the anatase polymorphic form did not persist anymore (Figure 4c), most likely because the increase of the almost amorphous nanotubes hinders the agglomeration of TiO2 particles [14,15,16,17,18] (see Supplementary Materials for details).
XPS analyses showed the expected surface atomic concentration of composites (Table 4). Notably, from both atomic percentages and high-resolution N1s signals (Figure S3) emerged that PEI-MWCNTs-TiO2 composite did not undergo to a sensible variations of its surface composition after catalytic reaction. The N1s signal could be curve fitted with two components: a dominant component at 400.5 ± 0.2 eV ascribed to amino groups and a minor component centred at 402.2 ± 0.2 eV that could be due to protonated amino groups or to amino groups involved in hydrogen bonding. This is a clear evidence of photocatalyst stability under the reaction conditions.
SEM images of samples 1A and 4C (Figure S4) showed heterogeneous samples consisting of MWCNTs randomly dispersed into TiO2 agglomerates. A high level of magnification (Figure S4(D)) highlights the close interfacial contact between nanotubes and TiO2 which is crucial for narrowing of titania bandgap and consequently for the enhancement of catalytic activity [48].
UV-Vis reflectance spectra of TiO2, TiO2@MWCNTs (1C) and TiO2@PEI-MWCNTs (4C) recorded in absorption mode are presented in Figure 5. As expeted, all hybrid materials showed a higher light absorption capability in the UV region below 400 nm, due to the characteristic absorption of TiO2. Remarkably, spectra of 1C and 4C appear to be quite similar, displaying the same red shift effect caused by the incorporation of both nanotubes alone and PEI-modified-CNTs into TiO2 [49,50,51]. This means that the formation of covalent bonds between MWCNTs and PEI in 4C does not introduce significant modifications of graphite-like structure of nanotubes. However, the composite 4C showed a more intense absorption underneath 350 nm, maybe due to the auxochrome effect (mainly n→σ* electronic transitions) of amino and hydroxyl groups linked on nanotubes surface. This effect could explain the enhanced photoreducing power displayed by composite 4C in the photoreductionof the organic dye UBA in the UV range (see mechanistic insights paragraph).

3.3. Phocatalytic Experiments

Photocatalytic conditions were chosen according to the goal of this study: the development of a metal free catalyst system that mimics the natural photosynthetic process, i.e., ambient temperature, sunlight radiation and water as the hydrogen source.
As a further aim of this work, we attempted to investigate the influence of radiation source on photocatalysis using two different emitting lamps: (i) the SANOLUX lamp, displaying a higher radiance in the near UV (315–400 nm) and the Xe-Halogen lamp, possessing the major emission power in the visible range (400–700 nm, see Figure S6 in Supplemetary Materials).
Photoreduction was performed in a water phase suspension (20 mL) of the solid catalyst (with the loading in the range of 7.5–30, and monitoring reaction parameters and species produced in both the liquid solution and in the gas phase of the reactor head space [43] (see Figure S5).
Argon was initially bubbled for 30 min, to avoid the presence of air, then CO2 for approximately 60 min, to saturate the reaction mixture, upon which suspension was irradiated for 5 h under vigorous stirring at room temperature. Initial pH value of solution after bubbling was found to be equal to 4.78, and raised to 5.80 after reaction.
Under the chosen conditions, nanocomposites proved to be active in converting CO2 into formic and acetic acids (Scheme 2), while neither simple PEI-grafted nanotubes nor bare TiO2 displayed appreciable activity (Table 5, runs 1–2).
The optimal irradiaton time of 5 h was ascertained by monitoring photoreduction in the first 7 h of reaction (Figure 6). Results showed that prolonged reaction times(>5 h) led to the decrease of yield in formic acid with the corresponding increment of acetic acid. A plausible explanation could be related to the partial transformation of HCOOH into CH3COOH by reaction with methyl radicals (CH3), according to the general mechanism proposed by S. Sharifnia et al. [52].
Composites 1A and 1C beharing unmodified MWCNTs gave formic acid as the major product (Table 5, runs 3–4). In addition, photoreducing power, especially the one leading to formic acid, increased with increasing the percentage of PEI-grafted nanotubes in the composite reaching the maximum level at about 30% (sample 4C, Table 5, runs 5–7).
The head space gas phase was monitored during reaction by means of GC analyses using a specific Barrier Ionization Discharge (BID) detector for revealing the reaction by-products.
Sampling of the gaseous phase above the reaction solution at different time intervals showed a constant composition consisting essentially of O2 (2%), Argon (5%) and CO2 (93%). Neither CO, nor H2 or other gaseous by-products (methane, ethane etc.) were detected during reaction. Notably, the light source proved to have a profound influence on the reaction selectivity: Xe-Halogen lamp (emitting primarily into the visible region) privileged the formation of formic acid, while SANOLUX lamp (with a main radiance in the near UV) favoured the formation of acetic acid (Table 5, runs 8–9).
Catalyst loading affected reaction in a predictable manner. Its increment increased the light scattering, thus limiting photoreducing process. As a consequence, despite the use of a threefold amount of solid catalyst, yields remained almost unchanged (Table 5, runs 11–14).

3.4. Catalyst Recycling

Stability and robustnes of our nanocatalysts were evaluated by means of recycling experiments (Figure 7). After each run the catalyst powder was recovered by filtration, washed with distilled methanol and water, and then dried under vacuum. Results evidenced a fair to good catalyst stability, with only a little loss of efficiency observed after the first cycle.

3.5. Mechanistic Insights

The photocatalytic process of CO2 reduction follows a relative unknown and complex mechanism leading to different products at the same time. Among them, CO, CH3OH, HCOOH, CH4, HCHO, CH3COOH and other light hydrocarbons are mainly observed, with a selectivity affected by a great number of factors [52].
We do not have elements to propose specific mechanisms, but can rationalize in the following points our experimental results attempting also to explain the remarkable enhancement of activity that polyamine modification of TiO2/MWCNTs nanocomposites can lead in CO2 photoreduction:
(i) Firstly, the detection of O2 into the head space of photoreactor can be considered a clear evidence that water is the sacrificial reductant for CO2.
(ii) Secondly, the high chemisorption capacity of TiO2@PEI-MWCNTs (4C) (18 mLCO2/g) is most probably the key reason for the its enhanced photoreducing ability, due to kinetic effects. Indeed, reaction of CO2 with NH2 groups forms carbamate, thus leading to the activation of carbon dioxide, because carbamate is believed to have a higher reactivity than the linear CO2 molecule (Figure 8) [24]. This assumption is corroborated by FT-IR analyses (Figure 9) of (4C) under photocatalytic conditions before and after CO2 bubbling, in which the peak at 1489 cm−1 appeared that can be attributed to the carbamate COO stretching [53,54].
(iii) Thirdly, an electronic effect of PEI could also be invoked in the UV range. It has been extensively approved that MWCNTs can narrow the band gap of TiO2 extending light absorption to longer wavelength region. The red shift observed in Figure 5 confirms such a hypothesis. In addition, due their graphite-like structure, MWCNTs are considered as a channel for electron storage, functioning as electron acceptors from higher conduction band of TiO2, thus inhibiting the recombination rate of electron-hole pairs through the transfer of electrons [24]. This is extremely crucial as the slower recombination rate leaves more holes in TiO2, promoting higher oxidation rate of water and thus enhancing reduction of CO2 (Figure 10).
In this context, it can be assumed that PEI-grafting, from one hand, does not modificate the graphite-like structure of CNTs thus allowing them to continue their action of narrowing the band gap of titania, while, form the other hand, can enhance the photocatalytic activity of TiO2 into the UV range due to the auxochrome effect.
Notably, lowering of crystallinity experienced by TiO2 as a consequence of hybridization (Figure 4c) does not influence catalytic performance, as this detrimental effect is counterbalanced by the enhancement of both the electron scavenging and CO2 capture capacity of nanocomposite by virtue of PEI-CNTs conjugation.
(iv) Searching for further confirmations on the effect on photocatalytic activity of PEI-conjugation with TiO2/MWCNTs composites, we investigated the photoreductionof the organic dye UBA, (Scheme 3) a model substrate commonly used to investigate electron transfer reactions [18,44,45]. Irradiation was performed with UV light using a mercury lamp (λ > 250 nm) and photoreduction was checked monitoring the colour change from blue (the colour of UBA anthraquinonic structure) to yellow (due to UBA reduced form).
Differences in absorbance (ΔAbs) acquired at 587 nm as a function of irradiation time were reported (Figure 11) [44,45]. Results clearly evidenced a higher reducing capability of the TiO2@PEI-MWCNTs (4C) compared to the bare TiO2. Indeed, with 4C as catalyst, an almost complete photoreduction of UBA was observed in the first 30 min of reaction, with the ΔAbs value of 0.98. After that, the ΔAbs value reached a plateau.
Conversely, with bare TiO2, the ΔAbs was detected to be 0.6 indicating that titania alone can promote UBA photoreduction up to the 60% in the first 30 min of irradiation. Next, despite prolonged irradiation the ΔAbs remained constant.
Two further control experiments were performed using PEI-MWCNTs (4) and TiO2@MWCNTs (1C) sample as catalysts, respectively. The former resulted in a 30% photoreduction of UBA during the first 30 min of irradiation, while the latter gave rise to 56% of UBA photoreduction, displaying a reduction capacity comparable with that of bare TiO2 and lower than that observed for TiO2@PEI-MWCNTs (4C). This beneficial role played by the functionalization with PEI could be explained with the auxochrome effect in the UV region exerted by amino and hydroxyl groups of PEI-modified composites (clearly visible in the UV spectrum of Figure 5), and is in accordance with the accepted principles “the higher the light absorption, the more the photoexcited electron–hole pairs” or also “the higher the reflectance the higher the activity” [55].
In addition, the disappointing results of UBA reduction assisted by PEI-MWCNTs (4), pointed out that an efficient UBA photoreductionis promoted only in the presence of TiO2, especially upon its interaction with MWCNTs efficiently mediated by PEI. Remarkably, the sample TiO2-MWCNTs (1C) showed a lower photocatalytic efficiency respect to the TiO2@PEI-MWCNTs (4C), despite they have a comparable specific surface area (Table 3: 299.2 m2/g and 304.2 m2/g, respectively). Such a behaviour further highlights the beneficial role played by the functionalization of MWCNTs with the PEI in the achievement of a highly photoactive nanocomposite.
(v) Finally, a special attention deserves the photoreduction selectivity towards the two main photoreduction products HCOOH/CH3COOH. Results in Table 5 clearly show that formation of HCOOH increases with increasing of PEI-grafted MWCNTs percentage in the nanocomposite, with the best yields reached with 30% ca. of carbon dopants (catalyst 4C, Table 5, runs 7–8, 14). This trend is in line with the above mentioned assumptions.
More difficult is the rationale for the formation of CH3COOH. This product is more rarely observed, even if is the major product in water suspension [56], like in our case, or using TiO2 doped with metals like Cu, Rh and Ru [56,57,58]. From results in Table 5 emerged that acetic acid formation depends on the nature of light source, with highest value reached using SANOLUX UV lamp (Table 5, run 9). This result indicates that formation of acetic acid is favoured by the UV-component of radiation and seems to be in accordance with the auxochrome effect of PEI into the UV region (Figure 5).
We do not have other elements explaining this phenomenon, and further efforts are needed to unravel the complex mechanistic aspects underlying the photocatalytic activity of these new materials.

4. Conclusions

In summary, we have found that polyethylenimine (PEI) anchored onto multiwalled carbon nanotubes can strongly enhance photocatalytic performances of TiO2/MWCNTs composites, rendering these materials efficient photocatalysts for CO2 conversion into formic and acetic acids. The simultaneous presence of PEI and CNTs is essential for catalysis, as demonstrated by the high sorbent capacity of TiO2@PEI-MWCNTs (4C) (18 mL/g) that enables both CO2 capture and activation, most probably via carbamate formation. Bleaching experiments corroborate in part the beneficial role of PEI in enhancing the photoreducing power of TiO2/MWCNTs composites in the UV range by means of a plausible auxochrome effect.
To the best of our knowledge, this is the first example in the literature in which amines-grafted CNTs materials can function as TiO2 co-catalysts for converting CO2 into carboxylic acids. We hope this work opens new avenues for carbon recycling using renewable sources.

Supplementary Materials

The following are available online at Detailed XRD, XPS, SEM analyses, CO2 photoreduction apparatus, Spectra of emission lamps (Figures S1–S6). Figure S1: Schematic representation of apparatus for measuring CO2 adsorption/desorption ability, Figure S2: XRD patterns of samples 4, 1A, 4A-B, Figure S3: High-resolution N1s signal, Figure S4: SEM image of (A) sample TiO2@MWCNTs 1A. SEM images of sample TiO2@PEI-MWCNTs 4C at (B) 2 μm, (C) 200 nm and (D) 100 nm of magnification level, Figure S5: Schematic of CO2 photoreduction apparatus, Figure S6: Emission spectra of (a) HRC UV-VIS lamp 300 W (Sanolux) and (b) Xe-Halogen lamp 400 W (Radium).


This research was supported by: Regione Puglia MIUR PON Ricerca e Competitività 20072013 Avviso 254/Ric. del 18/05/2011, Project PONa3 00369 “Laboratorio SISTEMA”, the Regione Puglia Project 3Z3VZ46 “RESTAUREO”, Apulia Region funded NanoApulia (MDI6SR) and Project RELA-VALBIOR, Network of Laboratories for Scientific Research (Italy). Project PON03PE_00004_1, “MAIND” MAteriali eco-innovativi e tecnologie avanzate per l’INDustria Manifatturiera e delle costruzioni. The authors wish to thank Ms Annarita Armenise for skilful assistance.

Author Contributions

M.C. performed the experiments of photoreduction of CO2; F.P performed the experiments of UBA, R.C. and V.M. performed the analysis of SEM; TEM, BET; F.F. performed the XPS and TGA analysis, A.F. and A.M performed the XRD analysis, R.C. and L.C. analyzed the data; C.F., L.D. and A.N. conceived and designed the experiments and wrote the paper.

Conflicts of Interest

The authors declare no conflict of interest.


  1. Kim, D.; Sakimoto, K.K.; Hong, D.; Yang, P. Artificial Photosynthesis for Sustainable Fuel and Chemical Production. Angew. Chem. Int. Ed. 2015, 54, 2–10. [Google Scholar] [CrossRef] [PubMed]
  2. Álvarez, A.; Bansode, A.; Urakawa, A.; Bavykina, A.V.; Wezendonk, T.A.; Makkee, M.; Gascon, J.; Kapteijn, F. Challenges in the Greener Production of Formates/Formic Acid, Methanol, and DME by Heterogeneously Catalyzed CO2 Hydrogenation Processes. Chem. Rev. 2017, 117, 9804–9838. [Google Scholar] [CrossRef] [PubMed]
  3. Inoue, T.; Fujishima, A.; Konishi, S.; Honda, K. Photoelectrocatalytic reduction of carbon dioxide in aqueous suspensions of semiconductor powders. Nature 1979, 277, 637–638. [Google Scholar] [CrossRef]
  4. Li, K.; Peng, B.; Peng, T. Recent Advances in Heterogeneous Photocatalytic CO2 Conversion to Solar Fuels. ACS Catal. 2016, 6, 7485–7527. [Google Scholar] [CrossRef]
  5. Guan, G.; Kida, T.; Yoshida, A. Reduction of carbon dioxide with water under concentrated sunlight using photocatalyst combined with Fe-based catalyst. Appl. Catal. B 2003, 41, 387–396. [Google Scholar] [CrossRef]
  6. Wang, W.N.; An, W.J.; Ramalingam, B.; Mukherjee, S.; Niedzwiedzki, D.M.; Gangopadhyay, S.; Biswas, P. Size and structure matter: enhanced CO2 photoreduction efficiency by size-resolved ultrafine Pt nanoparticles on TiO2 single crystals. J. Am. Chem. Soc. 2012, 134, 11276–11281. [Google Scholar] [CrossRef] [PubMed]
  7. Gui, M.M.; Chai, S.P.; Mohamed, A.R. Modification of MWCNT@ TiO2 core–shell nanocomposites with transition metal oxide dopants for photoreduction of carbon dioxide into methane. Appl. Surf. Sci. 2014, 319, 37–43. [Google Scholar] [CrossRef]
  8. Gui, M.M.; Wonga, W.M.P.; Chai, S.P.; Mohamed, A.R. One-pot synthesis of Ag-MWCNT@ TiO2 core–shell nanocomposites for photocatalytic reduction of CO2 with water under visible light irradiation. Chem. Eng. J. 2015, 278, 272–278. [Google Scholar] [CrossRef]
  9. Mele, G.; Annese, C.; D’Accolti, L.; De Riccardis, A.; Fusco, C.; Palmisano, L.; Scarlino, A.; Vasapollo, G. Photoreduction of Carbon Dioxide to Formic Acid in Aqueous Suspension: A Comparison between Phthalocyanine/TiO2 and Porphyrin/TiO2 Catalysed Processes. Molecules 2015, 20, 396–415. [Google Scholar] [CrossRef] [PubMed]
  10. Ong, W.-J.; Gui, M.M.; Chai, S.-P.; Mohamed, A.R. Direct growth of carbon nanotubes on Ni/ TiO2 as next generation catalysts for photoreduction of CO2 to methane by water under visible light irradiation. RSC Adv. 2013, 3, 4505–4509. [Google Scholar] [CrossRef]
  11. Xu, H.; Ouyang, S.; Liu, L.; Wang, D.; Kako, T.; Ye, J. Porous-structured Cu2O/TiO2 nanojunction material toward efficient CO2 photoreduction. Nanotechnology 2014, 25, 165402–165410. [Google Scholar] [CrossRef] [PubMed]
  12. Suna, Z.; Wanga, H.; Wua, Z.; Wang, L. g-C3N4 based composite photocatalysts for photocatalytic CO2 reduction. Catal. Today 2018, 300, 160–172. [Google Scholar] [CrossRef]
  13. Liu, Y.; Zhou, S.; Li, J.; Wang, Y.; Jiang, G.; Zhao, Z.; Liu, B.; Gong, X.; Duan, A.; Liu, Y.; et al. Photocatalytic reduction of CO2 with water vapor on surface La-modified TiO2 nanoparticles with enhanced CH4 selectivity. Appl. Catal. B. 2015, 168–169, 125–131. [Google Scholar] [CrossRef]
  14. Xia, X.-H.; Jia, Z.-J.; Yu, Y.; Liang, Y.; Wang, Z.; Ma, L.-L. Preparation of multi-walled carbon nanotube supported TiO2 and its photocatalytic activity in the reduction of CO2 with H2O. Carbon 2007, 45, 717–721. [Google Scholar] [CrossRef]
  15. Tian, L.; Ye, L.; Deng, K.; Zan, L. TiO2/carbon nanotube hybrid nanostructures: Solvothermal synthesis and their visible light photocatalytic activity. J. Solid State Chem. 2011, 184, 1465–1471. [Google Scholar] [CrossRef]
  16. Gao, B.; Chen, G.Z.; Puma, G.L. Carbon nanotubes/titanium dioxide (CNTs/TiO2) nanocomposites prepared by conventional and novel surfactant wrapping sol–gel methods exhibiting enhanced photocatalytic activity. Appl. Catal. B. 2009, 89, 503–509. [Google Scholar] [CrossRef]
  17. Cong, Y.; Li, X.; Qin, Y.; Dong, Z.; Yuan, G.; Cui, Z.; Lai, X. Carbon-doped TiO2 coating on multiwalled carbon nanotubes with higher visible light photocatalytic activity. Appl. Catal. B. 2011, 107, 128–134. [Google Scholar] [CrossRef]
  18. Kongkanand, A.; Kamat, P.V. Electron Storage in Single Wall Carbon Nanotubes. Fermi Level Equilibration in Semiconductor–SWCNT Suspensions. ACS Nano 2007, 1, 13–21. [Google Scholar] [CrossRef] [PubMed]
  19. Zhang, Y.; Tang, Z.-R.; Fu, X.; Xu, Y.-J. TiO2-Graphene Nanocomposites for Gas-Phase Photocatalytic Degradation of Volatile Aromatic Pollutant: Is TiO2-Graphene Truly Different from Other TiO2-Carbon Composite Materials? ACS Nano 2010, 4, 7303–7314. [Google Scholar] [CrossRef] [PubMed]
  20. Xie, S.; Zhang, Q.; Liu, G.; Wang, Y. Photocatalytic and photoelectrocatalytic reduction of CO2 using heterogeneous catalysts with controlled nanostructures. Chem. Commun. 2016, 52, 35–59. [Google Scholar] [CrossRef] [PubMed]
  21. Meng, X.; Ouyang, S.; Kako, T.; Li, P.; Liu, Q.; Wang, T.; Ye, J. Photocatalytic CO2 conversion over alkali modified TiO2 without loading noble metal cocatalyst. Chem. Commun. 2014, 50, 11517–11519. [Google Scholar] [CrossRef] [PubMed]
  22. Xie, S.J.; Wang, Y.; Zhang, Q.H.; Fan, W.Q.; Deng, W.P.; Wang, Y. Photocatalytic reduction of CO2 with H2O: significant enhancement of the activity of Pt–TiO2 in CH4 formation by addition of MgO. Chem. Commun. 2013, 49, 2451–2453. [Google Scholar] [CrossRef] [PubMed]
  23. Fu, Y.; Sun, D.; Chen, Y.; Huang, R.; Ding, Z.; Fu, X.; Li, Z. An Amine-Functionalized Titanium Metal–Organic Framework Photocatalyst with Visible-Light-Induced Activity for CO2 Reduction. Angew. Chem. Int. Ed. 2012, 51, 3364–3367. [Google Scholar] [CrossRef] [PubMed]
  24. Liao, Y.; Cao, S.W.; Yuan, Y.; Gu, Q.; Zhang, Z.; Xue, C. Efficient CO2 Capture and Photoreduction by Amine-Functionalized TiO2. Chem. Eur. J. 2014, 20, 10220–10222. [Google Scholar] [CrossRef] [PubMed]
  25. Liu, G.; Xie, S.; Zhang, Q.; Tian, Z.; Wang, Y. Carbon dioxide-enhanced photosynthesis of methane and hydrogen from carbon dioxide and water over Pt-promoted polyaniline–TiO2 nanocomposites. Chem. Commun. 2015, 51, 13654–13657. [Google Scholar] [CrossRef] [PubMed]
  26. Hsu, S.-C.; Lu, C.; Su, F.; Zeng, W.; Chen, W. Thermodynamics and regeneration studies of CO2 adsorption on multiwalled carbon nanotubes. Chem. Eng. Sci. 2010, 65, 1354–1361. [Google Scholar] [CrossRef]
  27. Mansoor, A.; Hoseini, V. Development of MWCNT@MIL-101 hybrid composite with enhanced adsorption capacity for carbon dioxide. Chem. Eng. J. 2012, 191, 326–330. [Google Scholar] [CrossRef]
  28. Lee, M.-S.; Park, S.-J. Silica-coated multi-walled carbon nanotubes impregnated with polyethyleneimine for carbon dioxide capture under the flue gas condition. J. Solid State Chem. 2015, 226, 17–23. [Google Scholar] [CrossRef]
  29. Dillon, E.P.; Crouse, C.A.; Barron, A.R. Synthesis, Characterization, and Carbon Dioxide Adsorption of Covalently Attached Polyethyleneimine-Functionalized Single-Wall Carbon Nanotubes. ACS Nano 2007, 2, 156–164. [Google Scholar] [CrossRef] [PubMed]
  30. Liu, Q.; Shi, J.; Wang, Q.; Tao, M.; He, Y.; Shi, Y. Carbon Dioxide Capture with Polyethylenimine-Functionalized Industrial-Grade Multiwalled Carbon Nanotubes. Ind. Eng. Chem. Res. 2014, 53, 17468–17475. [Google Scholar] [CrossRef]
  31. Yang, B.; Hu, H.; Yu, Q.; Zhang, X.; Lia, Z.; Lei, L. Pretreated multiwalled carbon nanotube adsorbents with amine-grafting for removal of carbon dioxide in confined spaces. RSC Adv. 2014, 4, 56224–56234. [Google Scholar] [CrossRef]
  32. Khalili, S.; Ghoreyshi, A.A.; Jahanshahi, M.; Pirzadeh, K. Enhancement of Carbon Dioxide Capture by Amine-Functionalized Multi-Walled Carbon Nanotube. Clean Soil Air Water 2013, 41, 939–948. [Google Scholar] [CrossRef]
  33. Casiello, M.; Iannone, F.; Cotugno, P.; Monopoli, M.; Cioffi, N.; Ciminale, F.; Trzeciak, A.M.; Nacci, A. Copper(II)-catalysed oxidative carbonylation of aminols and amines in water: A direct access to oxazolidinones, ureas and carbamates. J. Mol. Cat. A. Chem. 2015, 407, 8–14. [Google Scholar] [CrossRef]
  34. Iannone, F.; Casiello, M.; Monopoli, A.; Cotugno, P.; Sportelli, M.C.; Picca, R.A.; Cioffi, N.; Dell’Anna, M.M.; Nacci, A. Ionic liquids/ZnO nanoparticles as recyclable catalyst for polycarbonate depolymerization. J. Mol. Cat. A Chem. 2017, 426, 107–116. [Google Scholar] [CrossRef]
  35. Annese, C.; Abbrescia, D.I.; Catucci, L.; D’Accolti, L.; Denora, N.; Fanizza, I.; Fusco, C.; La Piana, G. Site-dependent biological activity of valinomycin analogs bearing derivatizable hydroxyl sites. J. Pep. Sci. 2013, 19, 751–757. [Google Scholar] [CrossRef] [PubMed]
  36. Lopalco, A.; Stella, V.J. Effect of molecular structure on the relative hydrogen peroxide scavenging ability of some α-keto carboxylic acids. J. Pharm Sci. 2016, 105, 2879–2885. [Google Scholar] [CrossRef] [PubMed]
  37. Dentuto, P.L.; Catucci, L.; Cosma, P.; Fini, P.; Agostiano, A.; D’Accolti, L.; Trevithick-Sutton, C.C.; Foote, C.S. Effect of cyclodextrins on the physicochemical properties of chlorophyll a in aqueous solution. J. Phys. Chem. B 2005, 109, 1313–1317. [Google Scholar] [CrossRef] [PubMed]
  38. Annese, C.; D’Accolti, L.; Filardi, R.; Tommasi, I.; Fusco, C. Oxidative cleavage of lactams in water using dioxiranes: an expedient and environmentally-safe route to ω-nitro acids. Tet. Lett. 2013, 54, 515–517. [Google Scholar] [CrossRef]
  39. D’Accolti, L.; Annese, C.; De Riccardis, A.; De Giglio, E.; Cafagna, D.; Fanelli, F.; Fusco, C. Dioxirane-Mediated Heterogeneous Epoxidations with Potassium Caroate: A Solid Catalyst Bearing Anchored Ketone Moieties. Eur. J. Org. Chem. 2012, 24, 4616–4621. [Google Scholar] [CrossRef]
  40. Annese, C.; D’Accolti, L.; Fusco, C.; Curci, R. Selective Hydroxylation of Methane by Dioxiranes under Mild Conditions. Org. Lett. 2011, 13, 2142–2144. [Google Scholar] [CrossRef] [PubMed]
  41. Annese, C.; D’Accolti, L.; Armuzza, V.; Da Ros, T.; Fusco, C. Epoxidation of multi-walled carbon nanotubes by organocatalytic oxidation. Eur. J. Org. Chem. 2015, 3063–3068. [Google Scholar] [CrossRef]
  42. Annese, C.; D’Accolti, L.; Giambastiani, G.; Mangone, A.; Milella, A.; Tuci, G.; Fusco, C. Tunable epoxidation of single-walled carbon nanotubes by isolated methyl(trifluoromethyl)dioxirane. Eur. J. Org. Chem. 2014, 8, 1666–1671. [Google Scholar] [CrossRef]
  43. Mele, G.; Annese, C.; De Riccardis, A.; Fusco, C.; Palmisano, L.; Vasapollo, G.; D’Accolti, L. Turning lipophilic phthalocyanines/TiO2 composites into efficient photocatalysts for the conversion of CO2 into formic acid under UV–Vis light irradiation. Appl. Cat. A 2014, 481, 169–172. [Google Scholar] [CrossRef]
  44. Cozzoli, P.D.; Fanizza, E.; Comparelli, R.; Curri, M.L.; Agostiano, A.; Laub, D.L. Role of Metal Nanoparticles in TiO2/Ag Nanocomposite-Based Microheterogeneous Photocatalysis. J. Phys. Chem. B 2004, 108, 9623–9630. [Google Scholar] [CrossRef]
  45. George, C.; Dorfs, D.; Bertoni, G.; Falqui, A.; Genovese, A.; Pellegrino, T.; Roig, A.; Quarta, A.; Comparelli, R.; Curri, M.L.; Cingolani, R.; Manna, L. A Cast-Mold Approach to Iron Oxide and Pt/Iron Oxide Nanocontainers and Nanoparticles with a Reactive Concave Surface. J. Am. Chem. Soc. 2011, 133, 2205–2217. [Google Scholar] [CrossRef] [PubMed]
  46. Aviles, F.; Cauich-Rodrıguez, J.V.; Moo-Tah, L.A.; May-Pat, A.; Vargas-Coronado, R. Evaluation of mild acid oxidation treatments for MWCNT functionalization. Carbon 2009, 47, 2970–2975. [Google Scholar] [CrossRef]
  47. Shen, X.; Du, H.; Mullins, R.H.; Kommalapati, R.R. Polyethylenimine Applications in Carbon Dioxide Capture and Separation: From Theoretical Study to Experimental Work. Energy Technol. 2017, 5, 822–833. [Google Scholar] [CrossRef]
  48. Miranda, S.M.; Romanosc, G.E.; Likodimosc, V.; Marquesa, R.R.N.; Favvasc, E.P.; Katsarosc, F.K.; Stefanopoulosc, K.L.; Vilarb, V.J.P.; Faria, J.L.; Falarasc, P.; et al. Pore structure, interface properties and photocatalytic efficiency ofhydration/dehydration derived TiO2/CNT composites. Appl. Catal. B Environ. 2014, 147, 65–81. [Google Scholar] [CrossRef]
  49. Natarajan, T.S.; Lee, J.Y.; Bajaj, H.C.; Jo, W.-K.; Tayade, R.J. Synthesis of multiwall carbon nanotubes/TiO2 nanotube composites with enhanced photocatalytic decomposition efficiency. Catal. Today 2017, 282, 13–23. [Google Scholar] [CrossRef]
  50. Gui, M.M.; Chai, S.-P.; Xub, B.-Q.; Mohamed, A.R. Visible-light-driven MWCNT@TiO2 core–shell nanocomposites and the roles of MWCNTs on the surface chemistry, optical properties and reactivity in CO2 photoreduction. RSC Adv. 2014, 4, 24007–24013. [Google Scholar] [CrossRef]
  51. Chen, Y.; Bian, J.; Qi, L.; Liu, E.; Fan, J. Efficient Degradation of Methylene Blue over Two-Dimensional Au/TiO2 Nanosheet Films with Overlapped Light Harvesting Nanostructures. J. Nanomater. 2015, 16, 254. [Google Scholar] [CrossRef]
  52. Karamian, E.; Sharifnia, S. On the general mechanism of photocatalytic reduction of CO2. J. CO2 Util. 2016, 16, 194–203. [Google Scholar] [CrossRef]
  53. Tumuluri, U.; Isenberg, M.; Tan, C.-S.; Chuang, S.S.C. In situ infrared study of the effect of amine density on the nature of adsorbed CO2 on amine-functionalized solid sorbents. Langmuir 2014, 30, 7405–7413. [Google Scholar] [CrossRef] [PubMed]
  54. Wilfong, W.C.; Srikanth, C.S.; Chuang, S.S.C. In situ ATR and DRIFTS studies of the nature of adsorbed CO2 on tetraethylenepentamine films. ACS Appl. Mater. Interfaces 2014, 6, 13617–13626. [Google Scholar] [CrossRef] [PubMed]
  55. Xu, Y.-H.; Wang, L.-Y.; Zhang, Q.; Zheng, S.-J.; Li, X.-J.; Huang, C. Correlation between photoreactivity and photophysics of sulfated TiO2 photocatalyst. Mater. Chem. Phys. 2005, 92, 470–474. [Google Scholar] [CrossRef]
  56. Nazimek, B.; Czech, B. Artificial photosynthesis-CO2 towards methanol. IOP Conf. Ser. Mater. Sci. Eng. 2011, 19, 012010. [Google Scholar] [CrossRef]
  57. Srinivas, B.; Shubhamangala, B.; Lalitha, K.; Reddy, P.A.K.; Kumari, V.D.; Subrahmanyam, M.; De, B.R. Photocatalytic Reduction of CO2 over Cu-TiO2/Molecular Sieve 5A Composite. Photochem. Photobiol. 2011, 87, 995–1001. [Google Scholar] [CrossRef] [PubMed]
  58. Ishitani, O.; Inoue, C.; Suzuki, Y.; Ibusuki, T.J. Photocatalytic reduction of carbon dioxide to methane and acetic acid by an aqueous suspension of metal-deposited TiO2. Photochem. Photobiol. A Chem. 1993, 72, 269–271. [Google Scholar] [CrossRef]
Figure 1. Synthesis of amine-grafted carbon nanotubes 3-4.
Figure 1. Synthesis of amine-grafted carbon nanotubes 3-4.
Materials 11 00307 g001
Figure 2. FT IR spectra mixing spectroscopic grade KBr of PEI-MWCNTs (4).
Figure 2. FT IR spectra mixing spectroscopic grade KBr of PEI-MWCNTs (4).
Materials 11 00307 g002
Figure 3. (a) TGA profiles of MWCNTs 1-4’; TEM images of (b) PEI-MWCNTs (4) and (c) p-MWCNTs (1).
Figure 3. (a) TGA profiles of MWCNTs 1-4’; TEM images of (b) PEI-MWCNTs (4) and (c) p-MWCNTs (1).
Materials 11 00307 g003
Scheme 1. Procedure for hybrid nanocomposites preparation.
Scheme 1. Procedure for hybrid nanocomposites preparation.
Materials 11 00307 sch001
Figure 4. XRD patterns of samples (a) 4; (b) 1A; (c) 4A-B.
Figure 4. XRD patterns of samples (a) 4; (b) 1A; (c) 4A-B.
Materials 11 00307 g004aMaterials 11 00307 g004b
Figure 5. Absorbance spectra in Kubelka-Munk units of photocatalytic materials.
Figure 5. Absorbance spectra in Kubelka-Munk units of photocatalytic materials.
Materials 11 00307 g005
Scheme 2. Photoreduction of carbon dioxide.
Scheme 2. Photoreduction of carbon dioxide.
Materials 11 00307 sch002
Figure 6. Monitoring of yields versus time in photocatalysis with composite 4C (experimental conditions of run 7, Table 5).
Figure 6. Monitoring of yields versus time in photocatalysis with composite 4C (experimental conditions of run 7, Table 5).
Materials 11 00307 g006
Figure 7. Recycling of photocatalyst nanocomposite 4C.
Figure 7. Recycling of photocatalyst nanocomposite 4C.
Materials 11 00307 g007
Figure 8. Activation of CO2 in photoreduction by PEI through carbamate formation.
Figure 8. Activation of CO2 in photoreduction by PEI through carbamate formation.
Materials 11 00307 g008
Figure 9. FT-IR images of TiO2@PEI-MWCNTs (4C) under photocatalytic conditions (a) before and (b) after CO2 bubbling.
Figure 9. FT-IR images of TiO2@PEI-MWCNTs (4C) under photocatalytic conditions (a) before and (b) after CO2 bubbling.
Materials 11 00307 g009
Figure 10. Effect of PEI conjugation on separation of photogenerated electron–hole pairs for TiO2@PEI-MWCNTs nanocomposite.
Figure 10. Effect of PEI conjugation on separation of photogenerated electron–hole pairs for TiO2@PEI-MWCNTs nanocomposite.
Materials 11 00307 g010
Scheme 3. photoreduction of UBA.
Scheme 3. photoreduction of UBA.
Materials 11 00307 sch003
Figure 11. Time course of UBA bleaching monitored at 587 nm. Data are reported as mean value of three replicates ± standard deviation.
Figure 11. Time course of UBA bleaching monitored at 587 nm. Data are reported as mean value of three replicates ± standard deviation.
Materials 11 00307 g011
Table 1. Preparation of nanocomposites 1A, 1C and 4A-C.
Table 1. Preparation of nanocomposites 1A, 1C and 4A-C.
NanocompositeMWCNTsAmount of MWCNTs (mg)TiCl4/HCl Mother Solution (mL)Weight of Nanocomposite (g)% (w/w) of PEI-MWCNTs in the Hybrid a
TiO2 (blank)250
TiO2@MWCNTs (1A)p-MWCNTs (1)202501.00562.0%
TiO2@MWCNTs (1C)p-MWCNTs (1)5005001.665130%
TiO2@PEI-MWCNTs (4A)PEI-MWCNTs (4)202501.11521.8%
TiO2@PEI-MWCNTs (4B)PEI-MWCNTs (4)2005001.950810.3%
TiO2@PEI-MWCNTs (4C)PEI-MWCNTs (4)5005001.619730.9%
a Evaluated based on the weights of suspended MWCNTs and recovered nanocomposites.
Table 2. CO2 adsorption/desorption ability of amine-grafted MWCNTs.
Table 2. CO2 adsorption/desorption ability of amine-grafted MWCNTs.
Amine-Grafted MWCNTsN-Content (%) by elem. AnalysisAdsorbed CO2 at 25 °C
(mL·g−1) a
Desorbed CO2 at 80 °C
(mL·g−1) b
p-MWCNTs 11111
HMDA-MWCNTs 31.012424
PEI-MWCNTs 42.633535
a Adsorption time 6 h. b Desorption time 3 h (see Supplementary Materials for details).
Table 3. Hybrid nanocomposites preparation.
Table 3. Hybrid nanocomposites preparation.
Hybrid a% (w/w) of PEI-MWCNTs in the HybridBET Surface Area (m2/g)
1A (control)2.0% b176.7
1C (control)30% b299.2
a See Table 1 for details. b Unmodified MWCNTs were hybridized as control composites.
Table 4. XPS analyses of hybrid nanocomposites.
Table 4. XPS analyses of hybrid nanocomposites.
Surface Atomic Concentrations (%)
PEI-MWCNTs (4)85.8 ± 0.56.8 ± 0.27.4 ± 0.2
TiO2@PEI-MWCNTs (4C)55.2 ± 0.630.6 ± 0.63.7 ± 0.310.5 ± 0.3
TiO2@PEI-MWCNTs (4C) *59.8 ± 0.627.6 ± 0.53.3 ± 0.29.3 ± 0.3
* After reaction.
Table 5. Catalytic performance of TiO2@PEI-MWCNT hybrids in the photoreduction of CO2.
Table 5. Catalytic performance of TiO2@PEI-MWCNT hybrids in the photoreduction of CO2.
RunCat.% (w/w) of PEI-MWCNTs in HybridCat. Loading (mg/mL) aLight Source bPhotocatalytic Products (μmol·g−1 Cat.) c
HCOOHCH3CO2HTotal Carbonaceous
1PEI-MWCNTs (4)7.5H/S0.210.010.22
31A2.0% d7.5H/S2.670.383.05
41C30.0% d7.5H/S5.802.738.53
104C e30.9%7.5H/S0.0860.0120.096
a Catalyst loading is 150 mg or 500 mg dispersed in 20 mL of water solution. b S = SANOLUX HRC UV-VIS lamp 300 W; H = RADIUM Xe-Halogen lamp 400 W. Irradiation time 5 h. c Estimated by ionic chromatography. HCOOH and CH3COOH formation was neither detected in the dark conditions nor without photocatalyst. d Unmodified MWCNTs were hybridized as control composites. e Without CO2.

Share and Cite

MDPI and ACS Style

Fusco, C.; Casiello, M.; Catucci, L.; Comparelli, R.; Cotugno, P.; Falcicchio, A.; Fracassi, F.; Margiotta, V.; Moliterni, A.; Petronella, F.; et al. TiO2@PEI-Grafted-MWCNTs Hybrids Nanocomposites Catalysts for CO2 Photoreduction. Materials 2018, 11, 307.

AMA Style

Fusco C, Casiello M, Catucci L, Comparelli R, Cotugno P, Falcicchio A, Fracassi F, Margiotta V, Moliterni A, Petronella F, et al. TiO2@PEI-Grafted-MWCNTs Hybrids Nanocomposites Catalysts for CO2 Photoreduction. Materials. 2018; 11(2):307.

Chicago/Turabian Style

Fusco, Caterina, Michele Casiello, Lucia Catucci, Roberto Comparelli, Pietro Cotugno, Aurelia Falcicchio, Francesco Fracassi, Valerio Margiotta, Anna Moliterni, Francesca Petronella, and et al. 2018. "TiO2@PEI-Grafted-MWCNTs Hybrids Nanocomposites Catalysts for CO2 Photoreduction" Materials 11, no. 2: 307.

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop