Water is an essential element for life. The availability of drinking water is threatened mainly by over-exploitation of water sources and excessive pollution. According to the 2019 World Health Organization report, in 2017, 29% of the global population lacked “safely managed drinking water” meaning water at home, available, and safe [1]. Presence of harmful compounds in water is mainly due to industrial, agricultural, and domestic activities [2] and creates problems directly or indirectly to the flora and fauna and consequently also to mankind. Moreover, this type of pollution has negative effects not only on health, but also from a socio-economic perspective [3, 4]. Two viable solutions against pollutants are their recovery through porous, high-surface, adsorbent materials that can be easily separated from the reaction environment (e.g., by centrifugation or by fixing it onto a substrate) [5, 6] or their neutralization and dissociation via chemical reactions of photocatalysis. Activated carbon, clay minerals, zeolites and polymers are some of the most utilized porous and adsorbent materials [7,8,9] whereas TiO2, ZnO, CeO2 ZrO2 and WO3 are chosen for their photocatalytic activity [10,11,12], or more in general, in the catalysis of chemical reactions [13,14,15].

Among the latter, TiO2 has attracted a great interest in the scientific community. This material is chemically stable, non-toxic and low cost [16] and it is used in the degradation of harmful and organic compounds [17,18,19,20] through its photoactivity triggered by ultraviolet light (UV), which generates electron-gap pairs responsible for the production of free radicals. Moreover, titanium dioxide is well known also for its mechanical and optical properties [21,22,23] which are applied in several fields, such as energetic, environmental, antibacterial and material science [24].

It has a compact crystalline structure and exists in three phases: anatase, rutile and brookite. It can be synthesized by several chemical [25,26,27,28] and physical [29, 30] techniques in the form of nanoparticles (NPs) [31, 32] and thin films [33,34,35]. At low calcination temperatures (TC < 400 °C), it is amorphous and exhibits a porous structure but, to our best knowledge, there are no many studies that take into consideration this property for environment applications. TiO2-based materials with adsorption capacity are generally made of composite materials [36,37,38,39]. This is also confirmed by a 2018 review analysing titania materials fixed on adsorbent substrates for the production of composite structures [40].

In this work, novel porous TiO2 nanopowders with a high and direct adsorption capacity, prepared by sol–gel method at low temperature (TC = 100 °C) and in an alkaline environment, were produced. We present a fast and simple synthesis of these NPs with an eco-friendly procedure, as it does not use toxic reagents. The chemical structure of the obtained materials has been characterised by Raman spectroscopy, scanning (SEM) and transmission electron (TEM) microscopies and thermogravimetric analysis (TGA) measurements. Methylene blue (MB) and diclofenac have been also used to study the adsorption behaviour of the TiO2 nanoparticles. The results have shown a very high and unusual seizing capacity of MB by the nanoparticles, a photocatalysis-independent phenomenon, due to the porous structure and high surface area of the nanoparticles. This adsorption is shown to be extremely fast and more advantageous than a photocatalysis process.

Materials and synthesis procedure

The titania (TiO2) nanopowders were synthesized by the sol–gel method. All the chemicals used were of reagent-grade purity and were purchased from Sigma-Aldrich. The production of titanium dioxide nanopowders was carried out in alkaline medium, using NH4OH, and in a neutral water medium as a comparison. In particular, for the alkaline solution preparation, 13.5 ml of NH4OH at 28–30% was added to 10 ml of ultrapure water milliQ. Subsequently, 1.5 ml of Titanium tetraisopropoxide (TTIP) was added to the solution and left in agitation for 60 min and then kept in dark for 24 h. The obtained precipitate was washed and collected two times with 2-propanol and other two times with ultrapure water, in an orbital shaker. After washing, the products were dried in an oven for 2 h at 50 °C. Such powders were then thermally treated for 3 h in a muffle at three different calcination temperatures TC = 100, 450 and 800 °C. Then, the powder samples were packed into glass holders without any other preparations.

Characterization techniques

Raman spectra were recorded with an InVia spectrometer, manufactured by Renishaw PLC (Gloucestershire, UK), equipped with optical microscope manufactured by Leica (Wetzlar, Germany). The excitation source was the 514.5 nm output of an Ar+ ions laser working at a maximum output power of 25 MW. All spectra were recorded using a resolution of 1.5 cm−1 over the spectral range of 150–3000 cm−1 at room temperature. X-Ray diffraction analyses were performed on titania powders, using a Rigaku Miniflex diffractometer, operating in step‐scan mode and employing Cu Kα radiation at 30 kV and 100 mA. The measurements were collected from 10° to 80°, with a 0.010° step size and a scan speed of 0.25° min−1.

SEM images were acquired by the scanning electron microscope JEOL JSM-5410LV with a Si(Li) windowless detector for the energy-dispersive X-ray microanalysis, an emission source of tungsten filament (W), a resolution of 3.5 nm, a magnification of 100–200,000× and an acceleration voltage of 0.5–30 kV. The samples were observed at low-vacuum mode, avoiding any kind of polishing and without covering by a conductive layer. Analysis was processed using Link Isis software by Oxford Instruments and Image Pro-Plus by Media Cybernetics.

TEM images of TiO2 materials were taken using Hitachi 7700 transmission electron microscope operated at 100 kV. This acceleration voltage was settled to obtain a sufficient resolution and minimal radiation damage of the material. Specimens for TEM observations were prepared by drop-casting of freshly solutions containing TiO2 nanoparticles onto standard carbon supported 600-mesh copper grid and drying slowly in air naturally.

Thermogravimetric analysis was used to monitor the mass variation of the titania powder samples. The system checks weight loss in function of time or temperature. The apparatus consisted of a Simultaneous Thermal Analyzer STA 409 by NETZSCH. Tests required a temperature ramp from 10 to 1100 °C, with a heating rate of 10 °C/min. Each sample was measured three times. The analysis was conducted in air atmosphere. The degradation rate can be known if the tangent at the curve is traced.

Adsorption tests

Adsorption tests were carried out on samples of TiO2 powders prepared in neutral and alkaline pH condition. The adsorption properties of the samples were evaluated by studying the variation in the methylene blue concentration in aqueous medium spectrophotometrically (using a PerkinElmer Lambda 45 UV–Vis spectrophotometer) via the solution absorbance in the Lambert–Beer regime. A quantity of 2.5 mg of TiO2 nanopowder was dispersed in 2 ml of the MB solution with a starting concentration of 1.5 × 10–5 M. Another test was conducted with diclofenac. Also in this case, 2.5 mg of TiO2 nanopowder was dispersed in 2 ml of diclofenac solution at a concentration of 1 × 10–4 M. The absorbance (A) of the solutions was measured at regular intervals (30 min), until the adsorption equilibrium was reached, recovering a fraction of the solution after centrifuging. Adsorption was studied monitoring the peak absorption of the MB at 665 nm and the peak absorption of diclofenac at 276 nm. Results are reported as A/A0, where A0 is the absorbance value of the solution a t = 0 min.

Results and discussion

Raman characterization

Raman spectra are reported in Fig. 1. The analysis revealed the typical active modes of anatase for the samples prepared in a neutral medium and calcinated at 100 °C and 400 °C. The peaks were observed at 151, 403, 518 and 639 cm−1 for the powder treated at 100 °C and at 144, 397, 516 and 636 cm−1 for that at 400 °C, and are attributed [41] to the vibration symmetries Eg, B1g, A1g/B1g and Eg, respectively. The active mode shift at 151 cm−1 observed in the sample treated at 100 °C in neutral medium could be related to low crystallinity and to the presence of oxygen vacancies in the TiO2 structure, as reported in literature [42, 43]. The samples treated at the highest temperature (T= 800 °C) showed three optical phonon peaks of the rutile phase: a very low-intensity mode centred at 143 cm−1 and two high-intensity modes at 446 and 609 cm−1, related to the B1g, Eg and A1g symmetries, respectively. The band observed around 235 cm−1 is generally attributed to the two-photon scattering [44].

Fig. 1
figure 1

Raman spectra of TiO2 nanopowders prepared in neutral and alkaline media and treated at calcination temperatures (TC) of 100, 400 and 800 °C. The letters A and R indicate the anatase and rutile phases, respectively

Both TiO2 nanoparticles synthesized in neutral and alkaline environments showed similar structures at the Raman analysis. Only the powder treated at 100 °C and prepared in alkaline solution showed a strong amorphous structure, probably induced by the sol (nitrogen was introduced during the sol–gel preparation as ammonium) and by the low temperature, inadequate to induce the crystallization of the titanium dioxide. On the other hand, temperatures of 400 °C and 800 °C were sufficient to induce the crystallization (anatase and rutile, respectively) in the same basic environment.

TEM and SEM analyses

To study the morphology of nanoparticles, TEM and SEM observations of the nanopowders prepared in neutral and alkaline conditions and thermally treated at 100 °C and 400 °C were carried out. Under the transmission microscope, the alkaline low-temperature sample appeared as very thin sheets folded and/or rolled up along the edges (Fig. 2a). On the contrary, the sample prepared in neutral environment at low temperature (Fig. 2b) showed a granular structure typical of sol–gel synthesis.

Fig. 2
figure 2

TEM images of TiO2 nanoparticles prepared in alkaline (a) and neutral (b) environments, treated at temperature of 100 °C

In addition, the increase in temperature (TC = 400 °C) induced a drastic change in the nanoparticles morphology. The powders synthesized in neutral or alkaline environments developed, instead, a granular structure (Fig. 3a, b). We founded the same result at the highest temperature (TC = 800 °C) (images are not reported here).

Fig. 3
figure 3

TEM images of TiO2 nanoparticles prepared in alkaline (a) and neutral (b) environments, treated at temperature of 400°

The structure of the alkaline sample treated at 100 °C, observed at TEM, was studied in detail at SEM. Under the scanning microscope, nanoparticles revealed a highly porous nano-tubular structure (Fig. 4a–c).

Fig. 4
figure 4

a SEM images of TiO2 nanoparticles prepared in alkaline environments, treated at the temperature of 100 °C; b and c details of tubular structures with higher magnification

SEM and TEM analyses confirmed the extremely porous nature of the TiO2 NPs  with a large surface area.

Thermogravimetic analysis

Thermogravimetric analysis tests were carried out to study the mass variation as a function of the temperature and to indirectly acquire information regarding the surface area of the nanoparticles. Generally, a mass variation, observed in an incompatible temperature range with the phase transition temperature, may be related to desorption of molecules from the surface of the material, so the greater the change in mass, the greater the surface area of the material. The measurements were conducted on TiO2 powders prepared in neutral and alkaline environments at different temperatures (T= 100, 400 and 800 °C). The samples were heated up to 1100 °C and the mass variation vs temperature was measured. The resulting graphs are displayed in Fig. 5. Samples calcined at 800 °C did not highlight a change in mass, while those calcined at 400 °C showed only a slight decrease in mass (< 5%). Only the powders dried during preparation at 100 °C, revealed a greater decrease in mass: in particular, we found a mass loss of about 10% for those prepared in neutral environment and a more consistent decrease of 22.5% for the samples synthetized in alkaline medium. The mass variation occurred at temperatures in range between 20 and 200 °C, in which the molecules, such as water adsorbed to the surface [45], pass into the gas phase reducing the mass of the sample. Therefore, the change in mass is due to desorption of molecules from the surface and not to a phase change of titanium dioxide, which occurs at higher temperatures [46]. These results were in accordance with the high surface area observed by electron microscopy analyses.

Fig. 5
figure 5

Thermogravimetric analysis of TiO2 powders synthetized in neutral and alkaline environments at different temperatures (TC = 100, 400 and 800 °C)

Adsorption tests

Figure 6 shows the MB absorption kinetics of TiO2 nanopowders prepared in neutral and alkaline media, calcinated at different temperatures (T= 100, 400, 800 °C). The graph shows the absorbance values normalized with respect to the initial value (A/A0), as a function of time. All samples reached the adsorption equilibrium after about 30 min. Only one sample revealed a different behaviour from the others. Differently from the others, the nanopowder prepared in alkaline environment and calcinated at 100 °C showed a rapid drop in the absorbance value of the solution, “decolorizing” it in a few minutes.

Fig. 6
figure 6

Methylene blue adsorption kinetics of TiO2 powders synthetized in neutral and alkaline media, calcinated at different temperatures (T= 100, 400, 800 °C)

It was, therefore, studied in detail the kinetics of adsorption of this sample. To achieve the sample saturation, the solution was centrifuged, and the liquid phase was recovered. Subsequently, the nanopowder was dispersed in a fresh MB solution. Once again, the powder showed a rapid adsorption of the dye, completely absorbing the MB within 30 min. This effect was then studied for several times and, only after 12 cycles, the phenomenon demonstrated a slowdown, as shown in Fig. 7.

Fig. 7
figure 7

Methylene blue adsorption of TiO2 powder prepared at T= 100 °C in basic pH environment

The strong adsorption of the dye may be due to an effect of opposite surface charge, which guarantees the attraction between organic molecule and TiO2, to a high surface area of titania NPs or to a synergistic effect of these two factors. To understand the charge influence on the adsorption, a test with diclofenac (a molecule with an opposite charge to MB) was carried out.

Figure 8 shows the absorption kinetics of this molecule on TiO2 powder prepared at 100 °C in basic pH environment. In this case, the adsorption resulted much more limited and the system reached the equilibrium after 230 min. Therefore, the charge of the target molecule seems to play a role in this phenomenon.

Fig. 8
figure 8

Diclofenac adsorption kinetics of TiO2 powder prepared at 100 °C in basic pH environment

The obtained results are very interesting and have been compared with literature. Table 1 shows the adsorption performance comparison between our material and two found in recent papers. The comparison takes into account the different starting conditions in terms of concentration, amount of TiO2 used and exposure time. The TiO2 described in our work is capable of absorbing a good amount of dye in 30 min. This quantity is even greater taking into account that, after 30 min, the sample has not reached the saturation and, therefore, several cycles are needed to reach it, bringing the absorbed amount to rather high values.

Table 1 Adsorption performance comparison


In this work, TiO2 NPs with high adsorption capacity were synthetized with a simple and eco-friendly procedure. The powder prepared in basic environment and at low temperature (T= 100 °C) revealed a more complex and porous structure than other nanoparticles synthesized in neutral environment. TEM and SEM analyses highlighted also a high surface area. In addition, these nanoparticles showed a good affinity for methylene blue rather than diclofenac, indicating that the extreme adsorbing capacity founded is due to the synergistic effect of surface charge and surface area. According to these considerations, these titania-based materials can be effectively applied in the context of adsorption and recovery of pollutants from wastewaters.