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Photocatalytic degradation of methyl orange at different pH values by NaYF4:Yb3+,Tm3+@TiO2 microrod composite photocatalysts under NIR excitation

Yanna Tang* and Jia Zeng
Ningbo Polytechnic University, Ningbo, Zhejiang 315800, China. E-mail: 2015076@nbpt.edu.cn; Tel: +86-13736135197

Received 5th January 2026 , Accepted 23rd April 2026

First published on 29th May 2026


Abstract

In this work, NaYF4:Yb3+,Tm3+@TiO2 microrod composite photocatalysts were fabricated via a hydrothermal method combined with a two-step wet-chemical coating strategy. Scanning electron microscopy (SEM) and transmission electron microscopy (TEM) characterization demonstrated that the NaYF4:Yb3+,Tm3+ microrods (∼1.2 µm in length and ∼0.4 µm in width) were uniformly coated with a porous anatase TiO2 shell. For the optimal sample S3, the thickness of the TiO2 shell was approximately 10 nm, with the size of a single TiO2 nanoparticle being about 6 nm. Under excitation with a 980 nm near-infrared (NIR) laser (spot size: 2 cm × 2 cm, total power: 28 W, and effective power density: 7 W cm−2), the TiO2 shell could efficiently absorb the ultraviolet upconversion emission from the NaYF4:Yb3+,Tm3+ core, and fluorescence kinetic measurements confirmed that fluorescence resonance energy transfer (FRET) occurs between the core and the shell. Compared with hydrothermally treated NaYF4:Yb3+,Tm3+, the fluorescence lifetime of the Tm3+ 1I6 excited state (at 291 nm emission) in the composite decreased from 128 µs to 100 µs, with a reduction of approximately 21%; in contrast, and the lifetime of the Tm3+ 1G4 excited state (at 474 nm emission) increased from 413 µs to 456 µs, increasing by about 10%. Photocatalytic degradation experiments with methyl orange (MO, 10 mg L−1, 50 mL) as the target pollutant revealed that the pH value of the solution exerted a significant influence on the degradation efficiency. Under the experimental conditions of 1 mg mL−1 catalyst concentration and 70 W cm−2 excitation power density (catalyst dosage: 50 mg, room temperature, magnetic stirring at 500 rpm, and 30 min dark adsorption equilibrium), the composite exhibited the optimal photocatalytic performance in an acidic system at pH 2, where the decolorization efficiency of MO was significantly higher than that in the neutral system (pH 6.5) and alkaline system (pH 11). Moreover, the MO decolorization rate decreased sequentially with an increase in the pH value of the solution. This study confirms that the FRET process between NaYF4:Yb3+,Tm3+ and TiO2 is a crucial mechanism for enhancing the NIR-driven photocatalytic activity of composite photocatalysts.


1. Introduction

As a highly promising green technology, photocatalytic CO2 reduction can convert carbon dioxide into organic fuels, which can alleviate the greenhouse effect and realize the recycling of carbon resources.1,2 In the field of environmental protection, the antibacterial and disinfection capabilities of photocatalysis can effectively inactivate microorganisms, such as bacteria and viruses, thus ensuring environmental safety.3 In biomedicine, photodynamic therapy based on photocatalytic principles provides novel strategies for cancer treatment.

Currently, photocatalytic technology still faces several critical challenges.4,5 Most traditional photocatalysts can only absorb in the ultraviolet region of sunlight, leading to a low utilization rate of visible light, which accounts for a larger proportion of the solar spectrum.6,7 Additionally, the photogenerated electron–hole pairs are prone to rapid recombination, which reduces the quantum efficiency and restricts the improvement of photocatalytic performance.8 Meanwhile, the difficulty in separating and recovering photocatalysts from reaction systems also hinders their large-scale industrial application.

Rare-earth-doped upconversion nanoparticles can convert near-infrared light into ultraviolet/visible emission, offering a promising way to utilize NIR light.9 In our previous studies, we first achieved NIR-responsive photocatalysis using YF3:Yb3+,Tm3+/TiO2 core/shell nanoparticles and further developed NaYF4:Yb,Tm@TiO2 with high NIR-driven activity and an elucidated energy transfer mechanism.10,11To address the above issues, in this work, NaYF4:Yb3+,Tm3+@TiO2 microrod composite photocatalysts were prepared via a hydrothermal method. We systematically investigated the NIR-driven photocatalytic properties of the as-prepared microrod composites for methyl orange degradation at different solution pH values, and clarified the intrinsic mechanism of the enhanced photocatalytic activity from the perspective of energy transfer.

2. Preparation of NaYF4:Yb3+,Tm3+@TiO2 microcomposites

2.1. reagents and instruments

Reagents used in the experiment: Yttrium nitrate (Y(NO3)3, 99.999%), ytterbium nitrate (Yb(NO3)3, 99.999%), thulium nitrate (Tm(NO3)3, 99.999%), ethylenediaminetetraacetic acid (EDTA, analytical grade), sodium fluoride (NaF), tetrabutyl titanate (TBOT, analytical grade), absolute ethanol and deionized water.

Experimental instruments and equipment: electronic balance, high-speed centrifuge, bench-top ultrasonic cleaner, magnetic stirrer and stainless-steel reaction kettle with a polytetrafluoroethylene lining.

2.2 Preparation of NaYF4:Yb3+,Tm3+ microrods

Ethylenediaminetetraacetic acid (EDTA) was employed as a surface modifier and complexing agent to synthesize hexagonal-phase NaYF4:Yb3+,Tm3+ microrods via a hydrothermal method. The molar ratio of the rare earth (RE) ions Y3+:Yb3+:Tm3+ was precisely controlled at 79[thin space (1/6-em)]:[thin space (1/6-em)]20[thin space (1/6-em)]:[thin space (1/6-em)]1, corresponding to the molar percentages of 79.0 mol% Y3+, 20.0 mol% Yb3+ and 1.0 mol% Tm3+ in the RE ion component. The actual molar ratios of Y3+, Yb3+ and Tm3+ in the prepared microrods were verified by inductively coupled plasma atomic emission spectroscopy (ICP-AES). The test results showed that the actual molar percentages of the three RE ions were consistent with the preset feeding ratio (deviation <1%), confirming the accurate control of the RE ion doping ratio in the synthesis process.

The specific experimental procedure is as follows: 1 mmol of mixed rare earth nitrates (prepared strictly according to the above 79[thin space (1/6-em)]:[thin space (1/6-em)]20[thin space (1/6-em)]:[thin space (1/6-em)]1 molar ratio) and 1 mmol of EDTA were added to a specific volume of deionized water, and the mixture was stirred magnetically for about 30 minutes until a stable white complex was formed. Then, an aqueous solution containing 12 mmol of NaF was added dropwise to the above complex solution under continuous stirring, and the stirring was maintained for 1 hour to ensure uniform mixing. The resulting precursor solution was transferred to a 40 mL closed autoclave with a polytetrafluoroethylene lining, and the hydrothermal reaction was conducted at 180 °C for 12 hours. After the reaction was completed, the autoclave was cooled naturally to room temperature. The obtained white precipitate was washed several times with absolute ethanol and deionized water to remove residual reactants, and finally dried in a vacuum drying oven at 80 °C for 12 hours to obtain the pure NaYF4:Yb3+,Tm3+ microrod powder.

2.3 Preparation of NaYF4:Yb3+,Tm3+@TiO2 core–shell composites

The concentrations of the as-prepared NaYF4:Yb3+,Tm3+ microcrystals and tetrabutyl titanate (TBOT) in the reaction precursor solution were fixed at 2 mg mL−1 and 3 µL mL−1, respectively. Titania-coated NaYF4:Yb3+,Tm3+ core–shell particles were fabricated by regulating the hydrolysis and condensation reactions of titanium alkoxide in ethanol. Here, titanium n-butoxide (Ti(OBu)4) was employed as the Ti source because its hydrolysis rate is approximately 150 times slower than that of tetraethyl titanate (Ti(OEt)4), which is conducive to the formation of a uniform and compact TiO2 shell layer.

A typical coating procedure was carried out as follows: NaYF4:Yb3+,Tm3+ nanoparticles were uniformly dispersed in ethanol containing a trace amount of Lutensol ON50 aqueous solution under ultrasonication. Subsequently, titanium alkoxide dispersed in anhydrous ethanol was added dropwise to the above seed particle dispersion at a controlled rate under rigorous magnetic stirring, and the reaction was allowed to proceed at room temperature for 20 h to form the TiO2 shell precursor. To obtain crystalline TiO2 shells, the above precursor solution was transferred to a 40 mL autoclave, sealed, and subjected to hydrothermal treatment at 160 °C for 6 h. The resulting NaYF4:Yb3+,Tm3+@TiO2 core–shell product was collected by centrifugation, washed with distilled water and anhydrous ethanol several times to remove the unreacted titanium alkoxide and by-products, and then dried in an air-drying oven at 80 °C to a constant weight.

2.4 Preparation of core–shell microrods with different TiO2 shell thicknesses

For the controllable synthesis of NaYF4:Yb3+,Tm3+@TiO2 core–shell composites with different TiO2 shell thicknesses, the concentrations of NaYF4:Yb3+,Tm3+ microcrystals and tetraethyl titanate (Ti(OEt)4) in the reaction precursor solution were adjusted, and the corresponding feeding amounts are listed in Table 1.
Table 1 Concentrations of NaYF4:Yb3+,Tm3+ and Ti(OEt)4 in the reaction precursor solution
Sample NaYF4:Yb3+,Tm3+ (mg mL−1) Ti(OEt)4 (µL mL−1)
S1 10 3
S2 5 3
S3 2 3
S4 2 6


3. Characterization and analysis

The purity and phase structure of the resulting products were analyzed on a Rigaku model Ru-200b X-ray powder diffractometer (XRD) using nickel-filtered Cu Kα radiation (λ = 1.5406 Å) in the 2θ range from 20° to 70°. Their size and morphology were characterized using transmission electron microscopy (TEM, JEM 2010F) at an accelerating voltage of 100 kV. The samples for TEM investigations were prepared by first dispersing the particles in ethanol under ultrasonication and then depositing a drop of the suspension onto a copper TEM grid coated with a holey carbon film. Photoluminescence spectra were recorded at room temperature on a Hitachi F-4500 fluorescence spectrophotometer (1.0 nm for slit width and 400 V for PMT voltage) with excitation from a 980 nm diode laser.

3.1 Structure and morphology

3.1.1 XRD. The structure and morphology of the samples were analyzed through X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), and high-resolution transmission electron microscopy (HRTEM). Figures show the characterization results of the NaYF4:Yb3+,Tm3+ microcrystals and NaYF4:Yb3+,Tm3+@TiO2 composites. All measurements were performed at room temperature.

The crystal phase structure of the samples was analyzed using a Rigaku Ru-200b powder X-ray diffractometer (λ = 1.5406 Å) in the 2θ scanning range of 10° to 70°. Fig. 1(a) presents the XRD patterns of NaYF4:Yb3+,Tm3+ before and after TiO2 coating, with the standard reference patterns of hexagonal NaYF4 (JCPDS No. 16-0334) and anatase TiO2 (JCPDS No. 21-1272) overlaid for direct phase comparison. All the diffraction peaks of the pristine NaYF4:Yb3+,Tm3+ microrods perfectly match the standard pattern of hexagonal NaYF4 (JCPDS No. 16-0334), without any impurity diffraction peaks, indicating the high phase purity of the as-synthesized NaYF4:Yb3+,Tm3+. The sharp diffraction peaks with narrow full width at half maximum (FWHM) further confirm the excellent crystallinity of the hexagonal NaYF4 phase. For the NaYF4:Yb3+,Tm3+@TiO2 core–shell composites, a weak but distinct diffraction peak is observed at 2θ = 25.4°, which is matches well with the characteristic (101) diffraction peak of anatase TiO2 (JCPDS No. 21-1272). The relatively low intensity and broad FWHM of this TiO2 peak suggest the small particle size of the anatase TiO2 shell. Notably, the position and intensity of the main diffraction peaks of hexagonal NaYF4 in the composites remain unchanged, confirming that the hydrothermal coating and crystallization process of TiO2 do not alter the crystal phase structure of the NaYF4:Yb3+,Tm3+ core.


image file: d6ra00088f-f1.tif
Fig. 1 (a) XRD patterns of the pristine NaYF4:Yb3+,Tm3+ microrods and NaYF4:Yb3+,Tm3+@TiO2 core–shell composites, with the standard reference pattern of hexagonal NaYF4 (JCPDS No. 16-0334) and anatase TiO2 (JCPDS No. 21-1272) overlaid for phase identification. (b) XRD patterns of the NaYF4:Yb3+,Tm3+@TiO2 composite samples S1–S4, where the characteristic peak marked A corresponds to the (101) crystal plane of anatase TiO2 (JCPDS No. 21-1272), and the hexagonal NaYF4 (JCPDS No. 16-0334) standard reference pattern is overlaid as the reference for the main phase.

Fig. 1(b) shows the XRD patterns of composite samples S1–S4 with the hexagonal NaYF4 standard pattern (JCPDS No. 16-0334) overlaid. The results further verify that all the composite samples retain the pure hexagonal phase of NaYF4:Yb3+,Tm3+, and neither the TiO2 coating process nor the variation in TiO2 content induces a phase transformation of the NaYF4 core. With an increase in the titanium source concentration in the precursor solution, the intensity of the anatase TiO2 characteristic peak (2θ = 25.4°, JCPDS No. 21-1272, marked as A) gradually increases, which is consistent with the increase in TiO2 content in the core–shell composites.

3.1.2 SEM and TEM. The morphology and size of the samples were analyzed by scanning electron microscopy (SEM) and transmission electron microscopy (TEM). Fig. 2 shows the SEM and TEM images of the NaYF4:Yb3+,Tm3+ microcrystals and the NaYF4:Yb3+,Tm3+@TiO2 photocatalysts. Fig. 2(a) and (d) show the SEM and TEM images of the NaYF4:Yb3+,Tm3+,Tm microcrystals, respectively. It can be observed that when EDTA was used as the surfactant and chelating agent, the samples obtained by the hydrothermal method were microrods. They were approximately 1.2 µm in length and about 0.4 µm in width, and their surface was relatively smooth and flat. However, after compositing with TiO2 particles, the surface of the microrods changed from smooth to rough, as shown in Fig. 2(b) and (e). Fig. 2(c) and (f) show the enlarged views of Fig. 2(b) and (e), respectively. It can be clearly seen from these figures that the shell layer composed of porous TiO2 nanoparticles was closely deposited on the surface of the microrods, and the thickness of the shell layer is approximately 10 nm. The size of a single TiO2 nanoparticle is about 6 nm. Fig. 2(g) shows the local TEM image of a single microrod, and Fig. 2(h) shows the corresponding high-resolution transmission electron microscopy (HRTEM) image. Through calculation, the interplanar spacings of the particles in the shell layer were found to be 0.352 nm and 0.24 nm, which are consistent with the interplanar spacings of the {100} and {103} crystal planes of the anatase structure of TiO2, respectively, confirming that the TiO2 on the surface of the microrods has an anatase structure. Within the field of view, all the TiO2 nanoparticles were deposited on the surface of the microrods, and there was no phenomenon of secondary nucleation. Repeated experiments have demonstrated that the two-step wet chemical method we adopted for synthesizing the core–shell structured materials is very simple, effective, and easy to repeat.
image file: d6ra00088f-f2.tif
Fig. 2 SEM and TEM images of pristine NaYF4:Yb3+,Tm3+ microcrystals (a and d) and TiO2-coated NaYF4:Yb3+,Tm3+ composites (b–c), (e–f). (h) is the HRTEM image of (g).

Fig. 3 shows the TEM images of samples S1–S4. When a small amount of TBOT is added to the reaction precursor, a sparse TiO2 coating layer is formed on the surface of the micrometer crystals, as shown in Fig. 3(a). When the amount of TBOT in the reaction system is increased, a uniform and dense TiO2 coating layer is formed on the surface of the micrometer-sized crystals (Fig. 3(b)). When the amount of TBOT is further increased, the TiO2 shell layer is relatively uniform, and its thickness increases to about 15 nm (Fig. 3(c)). When the mass fraction of TiO2 in the reaction system is further increased, some of the TiO2 nanoparticles in the shell layer of the obtained composite material aggregate on the surface of the micrometer-sized rods (Fig. 3(d)).


image file: d6ra00088f-f3.tif
Fig. 3 TEM images of S1 (a), S2 (b), S3 (c) and S4 (d).

3.2 Discussion of the optical properties

3.2.1 Upconversion luminescence properties. The upconversion emission spectra of the samples were measured using a Hitachi F-4500 fluorescence spectrometer, with a 980 nm near-infrared semiconductor diode as the excitation source (excitation power: 100 mW, slit width: 1.0 nm, and PMT voltage: 400 V). Fig. 4 shows the upconversion fluorescence emission spectra of the NaYF4:Yb3+,Tm3+ microcrystals and the NaYF4:Yb3+,Tm3+@TiO2 composite materials. All the samples were normalized at the wavelength of 474 nm (1G43H6) to ensure the comparability of the luminescence intensity.
image file: d6ra00088f-f4.tif
Fig. 4 Upconversion emission spectra of the NaYF4:Yb3+,Tm3+ micrometer crystals before and after hydrothermal treatment and of the NaYF4:Yb3+,Tm3+@TiO2 composite material under 980 nm excitation.

Fig. 4 shows the upconversion fluorescence emission spectra of the NaYF4:Yb3+,Tm3+ microrods before and after hydrothermal treatment, and of the NaYF4:Yb3+,Tm3+@TiO2 composite material. The emission peaks all arise from the characteristic emissions of Tm3+ ions. The ultraviolet emission peaks at wavelengths of 291 nm, 350 nm, and 365 nm result from the 1I63H6, 1I63F4, and 1D23H6 radiative transitions of Tm3+ ions, respectively. The two blue-light emission peaks at 450 nm and 474 nm are ascribed to the 1D23F4 and 1G43H6 radiative transitions of Tm3+ ions. By observing the upconversion emission spectra, it can be seen that the ultraviolet upconversion luminescence efficiency of NaYF4:Yb3+,Tm3+ significantly increased after annealing. This is mainly due to the presence of surface organic groups with high vibrational-mode energies, such as –OH and –NH2, on the surface of the unmodified particles before hydrothermal treatment. These organic groups and surface defects can easily cause non-radiative transitions of the excited-state energy levels of RE ions, leading to the quenching of the luminescent centers. Hydrothermal treatment can effectively remove a large number of surface states, such as organic groups and surface defects, reducing the probability of non-radiative transitions in the excited state and protecting the luminescent centers. Therefore, the ultraviolet-visible upconversion luminescence efficiency of the hydrothermal-treated NaYF4:Yb3+,Tm3+ microrods is enhanced.

However, when comparing the upconversion fluorescence emission spectra of the micro-rods before and after being coated with TiO2, it is observed that under near-infrared excitation, the intensities of the ultraviolet upconversion emissions at 291 nm, 350 nm, and 365 nm with wavelengths less than 400 nm are significantly weakened. Especially, the intensity of the emission peak at 291 nm (1I63H6) is very weak, while the fluorescence intensities of the two blue-light emission peaks (at 450 nm and 474 nm) hardly change. This phenomenon indicates that there are physical interactions such as transfer between NaYF4:Yb3+,Tm3+ and TiO2, rather than simple surface modification of TiO2 on the upconversion luminescent particles.

Fig. 5(a) shows the upconversion luminescence spectra of NaYF4:Yb3+,Tm3+ microrods and sample S1 to S4 under the excitation of a 980 nm laser. Compared with the upconversion emission spectrum of NaYF4:Yb3+,Tm3+ microrods, the intensities of the upconversion emission peaks of samples S1–S4 in the blue-light region do not change significantly. However, in the ultraviolet band, the upconversion intensity decreases as the mass fraction of the TiO2 shell layer increase. This phenomenon can be attributed to two reasons: firstly, as the mass fraction of TiO2 in the composite material increases, the probability of re-absorption of upconverted ultraviolet light by the TiO2 shell layer effectively increases. Secondly, the increase in the mass fraction of TiO2 leads to an increase in the probability of energy transfer from Tm3+ ions in the 1I6 and 1D2 excited-state energy levels to the TiO2 shell layer in the composite material. Fig. 5(b) shows the upconversion luminescence spectra of sample S3 under different excitation light powers (50–130 mW). The intensities of all characteristic emission peaks of Tm3+ ions increase with the increase of the laser power, while the luminescence intensity at 291 nm (1I63H6) is still very weak. By analyzing Fig. 5(a) and (b) together, we conclude that the successive weakening of the ultraviolet upconversion luminescence intensities of the composite materials S1–S4 in Fig. 5(a) is caused by the increase in the mass fraction of TiO2, and has nothing to do with the intensity of the excitation light power.


image file: d6ra00088f-f5.tif
Fig. 5 (a) Upconversion luminescence spectra of the NaYF4:Yb3+,Tm3+ micrometer-sized crystals and samples S1–S4 under 980 nm laser excitation. (b) Upconversion spectra of the sample S3 under different excitation powers.
3.2.2 Absorption spectra. The absorption spectra of the samples were measured using a Shimadzu UV-3600 UV-vis-NIR spectrophotometer in a scanning range of ∼200–1200 nm at a scanning rate of 200 nm min−1. The test results are shown in Fig. 6. The transition of Yb3+ ions from 2F5/22F7/2 gives the samples a relatively large absorption cross-section near 980 nm. Therefore, the absorption peaks near 980 nm in the absorption spectra of NaYF4:Yb3+,Tm3+ and NaYF4:Yb3+,Tm3+@TiO2 are the characteristic absorption peaks of Yb3+ ions. In the absorption spectrum of the NaYF4:Yb3+,Tm3+@TiO2 composite material, in addition to the characteristic absorption peak of Yb3+ ions, there is a very strong absorption band near a wavelength of 400 nm, which is the characteristic absorption band of anatase-structured TiO2. This combined with the phenomenon that the presence of TiO2 in the upconversion spectrum significantly weakens the ultraviolet emission strongly illustrates that the weakening of the upconversion ultraviolet luminescence intensity is partly caused by radiation absorption and reabsorption in the TiO2 shell layer.
image file: d6ra00088f-f6.tif
Fig. 6 Absorption spectra of the NaYF4:Yb3+,Tm3+ micrometer-sized crystals and NaYF4:Yb3+,Tm3+@TiO2 composite materials.
3.2.3 Fluorescence decay curve. The energy migration process between upconversion and TiO2 in the NaYF4:Yb3+,Tm3+@TiO2 microcomposite material was analyzed through the fluorescence decay curves of the three excited-state energy levels of 1I6, 1D2 and 1G4 in Tm3+ ions. The fluorescence decay curves were measured using a Hitachi F-4500 fluorescence spectrometer at an excitation wavelength of λex = 953.6 nm and a time resolution of 0.1 µs.

Fig. 7 shows the fluorescence decay curves obtained at different emission peaks measured for the three excited states of Tm3+ ions in the NaYF4:Yb3+,Tm3+ microcrystals before (green) and after (blue) hydrothermal treatment and in the NaYF4:Yb3+,Tm3+@TiO2 composite material (red), respectively at the excitation wavelength λ = 953.6 nm. The detected emission peaks are located at 291, 345, 365, 450 and 474 nm, corresponding to the radiative transitions of 1I63H6, 1I63F4, 1D23H6, 1D23F4 and 1G43H6, respectively. Each fluorescence curve is composed of two parts: a rising edge and a falling edge. In the rising edge part, the fluorescence intensity rapidly increases to the maximum value, indicating that the energy transfer process from Yb3+ ions to Tm3+ ions is rapid and effective. In the falling part, as the ultraviolet-visible light radiative transition of the excited-state energy levels in Tm3+ ions occurs, the fluorescence intensity decays in a single-exponential function due to the ultraviolet-visible light radiative transition of the excited-state energy levels in Tm3+ ions.


image file: d6ra00088f-f7.tif
Fig. 7 Fluorescence decay curves of the three excited-state energy levels of 1I6, 1D2 and 1G4 of Tm3+ ions in the NaYF4:Yb3+,Tm3+ microcrystals before (green) and after (blue) hydrothermal treatment and in the NaYF4:Yb,Tm/TiO2 composite material (red). The detected peaks at (a) 291, (b) 345, (c) 365, (d) 450 and (e) 474 nm correspond to the radiative transitions of 1I63H6, 1I63F4, 1D23H6, 1D23F4 and 1G43H6, respectively, and the excitation wavelength (λ) is 953.6 nm.

The decay part was fitted with a single-exponential decay formula, and the fitting values of the fluorescence lifetime are shown in Table 2. For the detected peak at 291 nm (corresponding to the 1I63H6 radiative transition), the energy level lifetime of the 1I6 excited state increases by approximately 16% (from 110 µs to 128 µs). This is because the reduction of surface defects and organic groups on the surface of the microrods after hydrothermal treatment leads to a decrease in the non-radiative transition rate (W_NIR), thus increasing the fluorescence lifetime of the excited state. Compared with NaYF4:Yb,Tm after hydrothermal treatment, the fluorescence decay lifetime of the 1G4 energy level of Tm3+ ions in the NaYF4:Yb3+,Tm3+@TiO2 composite system increases by about 10% (from 413 µs to 456 µs), which is mainly because the TiO2 shell layer reduces the surface defects in the NaYF4 particles and decreases the probability of non-radiative transition of the 1G4 energy level. In contrast, the fluorescence lifetime of the 1I6 energy level decreases by about 21% (from 128 µs to 100 µs). This result confirms that there is an effective energy transfer process between the upconversion microrods and the TiO2 shell layer in the composite system. The energies of the 1I6 and 1D2 excited state energy level are greater than the bandgap width of TiO2, and thus the Tm3+ ions in these two energy levels directly transfer energy to TiO2, leading to the accelerated decay of the fluorescence lifetime, while the energy of the 1G4 energy level is less than the bandgap width of TiO2 and cannot transfer energy to TiO2, and thus its fluorescence lifetime is prolonged due to the reduction of surface defects.

 
I(t) = A1[thin space (1/6-em)]exp(−t/τ1) + A2[thin space (1/6-em)]exp(−t/τ2) (1.1)

Table 2 Fluorescence lifetime of the ions at different excited states in different samples (µs)
Sample 1I6 (µs) 1D2 (µs) 1G4 (µs)
291 nm 345 nm 365 nm 450 nm 474 nm
NaYF4:Yb3+,Tm3+ (before annealing) 110 115 150 148 387
NaYF4:Yb3+,Tm3+ (after annealing) 128 127 168 164 413
NaYF4:Yb3+,Tm3+@TiO2 100 112 134 142 456


The decay part is fitted with a formula, and the fitting values are shown in Table 2.

According to formula (1.1), the reduction of surface defects and organic groups on the surface of the microparticles after hydrothermal treatment leads to a decrease in the non-radiative transition rate (WNR), thus increasing the fluorescence lifetime of the excited state.

3.3 Standardized photocatalytic degradation experiments of methyl orange

3.3.1 Experimental setup and operation parameters. All experiments for the photocatalytic degradation of methyl orange (MO) were carried out in a customized temperature-controlled photocatalytic reaction system to ensure the reproducibility of the test results. The key experimental parameters and detailed operation steps are clearly specified as follows, in accordance with the reproducibility requirements for photocatalytic experiments.

The pH value of the solution has a significant impact on the photocatalytic degradation rate. For different reaction systems, the influence of the pH value on the catalytic efficiency also varies. Herein, the organic dye system of methyl orange (MO) was taken as the research object to study the photocatalytic activity of the NaYF4:Yb3+,Tm3+@TiO2 microcomposite material in aqueous solutions with different pH values.

MO is an azo organic dye compound that is relatively difficult to degrade. Its molecule has two main structural forms: the azo structure (Fig. 8(a)) and the quinoid structure (Fig. 8(b)). Under alkaline and neutral conditions, the MO aqueous solution appears yellow and orange, respectively, and at this time, the MO molecules are all in the azo structure; under acidic conditions, the solution appears red, and MO is in the quinoid structure. Therefore, it is representative to study MO as a model dye compound. Due to the different molecular structures, the characteristic absorption peaks of MO in acidic and neutral (or alkaline) solutions are located at wavelengths of 506 nm and 464 nm, respectively. Here, under the conditions of an equal amount of photocatalyst, the same light irradiation time and light source intensity, the photocatalytic activity of the composite material was studied at pH values of 2, 6.5 and 11. In the experiment, the pH value of the MO aqueous solution was adjusted using 0.1 M HCl and 0.1 M NaOH aqueous solutions. The concentration of the photocatalyst was 1 mg mL−1. The excitation power density was 70 W cm−2.


image file: d6ra00088f-f8.tif
Fig. 8 Molecular structure of MO in (a) neutral (orange-colored) and alkaline (yellow-colored) aqueous solutions featuring a typical azo structure. (b) Molecular structure of MO in an acidic (red-colored) aqueous solution, with a typical quinoid structure.
3.3.2 Photocatalytic degradation results and analysis. Fig. 9(a)–(c) show the change in the absorption spectra of MO with illumination time in aqueous solutions of different pH values when NaYF4:Yb3+,Tm3+@TiO2 is excited by NIR. It can be seen that the characteristic absorption peak intensity of MO decreases gradually with the extension of NIR irradiation time in all three pH systems, indicating that the composite catalyst has NIR-driven photocatalytic degradation performance for MO in different acid-base environments12. The absorption peak intensity of MO in the acidic system (pH = 2) decreases the fastest, followed by the neutral system (pH = 6.5), and the slowest in the alkaline system (pH = 11), indicating that the solution pH has significant impact on the photocatalytic degradation efficiency of the composite catalyst.

Fig. 9(d) shows the changes in curves of the ratio of the concentration of MO to the initial concentration (C/C0) with an increase in illumination time under different experimental conditions (no catalyst, only NaYF4:Yb3+,Tm3+ microrods, NaYF4:Yb3+,Tm3+@TiO2 composite at pH = 2, 6.5 and 11). The experimental results show that: (1) without the catalyst, the MO concentration has almost no change under NIR irradiation for 7 h, indicating that MO has no photolysis under 980 nm NIR light; (2) the pure NaYF4:Yb3+,Tm3+ microrods have almost no photocatalytic degradation effect on MO, with a decolorization efficiency of only about 5% after 7 h of irradiation, indicating that the upconversion material itself cannot degrade MO; and (3) the NaYF4:Yb3+,Tm3+@TiO2 composite catalyst exhibits a significant photocatalytic degradation performance, and the decolorization efficiency is highly dependent on the solution pH: the decolorization efficiency reaches 98.2% at pH = 2, 76.5% at pH = 6.5, and only 52.3% at pH = 11 after 7 h of NIR irradiation, which is consistent with the change trend of the absorption spectra (Fig. 9).


image file: d6ra00088f-f9.tif
Fig. 9 Change in the absorption spectrum of MO with the illumination time when the NaYF4:Yb3+,Tm3+@TiO2 photocatalyst is excited under NIR illumination in aqueous solutions of different pH values: (a) pH = 2, (b) pH = 6.5, and (c) pH = 11. (d) Change in the concentration ratio (C/C0) of methyl orange with an increase in the illumination time under different conditions: catalyst without illumination, illumination without catalyst, and illumination in the presence of the NaYF4:Yb3+,Tm3+@TiO2 composite material at different pH values.

For the MO organic dye system, the pH-dependent photocatalytic performance is mainly determined by two factors: on the one hand, the MO molecule exists in a quinoid structure under acidic conditions (pH = 2), which is more easily degraded by hydroxyl radicals (˙OH) than the azo structure in neutral/alkaline conditions. On the other hand, TiO2 is an amphoteric oxide, and its surface charge changes with the solution pH. Under acidic conditions, the TiO2 surface adsorbs H+ and becomes positively charged (TiOH2+), which can effectively adsorb the negatively charged MO molecules through electrostatic attraction, increasing the contact probability between MO molecules and the active species (˙OH) generated on the catalyst surfaces. Under alkaline conditions, the TiO2 surface adsorbs OH and becomes negatively charged (TiO), which produces Coulomb repulsion with the negatively charged MO molecules, reducing the adsorption amount of MO and thus decreasing the photocatalytic degradation efficiency. The surface charge of TiO2 under neutral conditions is close to zero, and thus, the optimal photocatalytic performance is observed between acidic and alkaline conditions.

 
TiOH + H+ ↔ TiOH2+ (1.2)
 
TiOH + OH ↔ TiO + H2O (1.3)

3.4 Post-reaction stability analysis

To evaluate the structural durability and reusability potential of the NaYF4:Yb3+,Tm3+@TiO2 core–shell photocatalysts in practical applications, the phase structure and surface chemical state of the S3 sample (with optimal photocatalytic performance) were characterized by X-ray diffraction (XRD) after the 12 h NIR-driven photocatalytic degradation of methyl orange (MO, pH = 2). The post-reaction catalyst was collected by centrifugation, washed thoroughly with deionized water and anhydrous ethanol to remove adsorbed MO molecules and reaction byproducts, and then dried at 80 °C in air prior to characterization, ensuring that no external impurities interfered with the test results.

Fig. 10 shows the XRD patterns of the NaYF4:Yb3+,Tm3+ and S3 samples after the photocatalytic reaction, with the standard reference patterns of hexagonal NaYF4 (JCPDS No. 16-0334) and anatase TiO2 (JCPDS No. 21-1272) overlaid for comparison. It can be observed that the XRD pattern of the post-reaction S3 sample is highly consistent with that of the fresh sample, where all characteristic diffraction peaks of hexagonal NaYF4 and anatase TiO2 remain well-resolved, with no obvious shifts in peak position, no significant reduction in peak intensity, and no new impurity diffraction peaks generated. The sharp diffraction peaks of NaYF4 and the weak characteristic peak of anatase TiO2 at 2θ = 25.4° are still clearly distinguishable, indicating that the core–shell crystal phase structure of NaYF4:Yb3+,Tm3+@TiO2 remains intact after the photocatalytic reaction. The high crystallinity of the composite effectively resists the structural damage caused by photochemical reactions and the acidic reaction environment (pH = 2), verifying the excellent phase stability of the photocatalyst during the degradation process.


image file: d6ra00088f-f10.tif
Fig. 10 Schematic of the energy transfer process among Yb3+, Tm3+ and TiO2, the reaction of photogenerated electrons and holes with organic molecules on the TiO2 surface to generate ˙OH radicals, and the energy level diagram under near-infrared (NIR) light excitation.

3.5 Five-cycle reusability test

To evaluate the practical applicability and long-term performance stability of the NaYF4:Yb3+,Tm3+@TiO2 core–shell photocatalyst in actual wastewater treatment, five-cycle reusability tests were conducted under the optimal photocatalytic conditions (pH = 2, 50 mg catalyst, 50 mL 10 mg L−1 MO, at room temperature, 500 rpm magnetic stirring, 30 min dark adsorption, and 980 nm NIR with 7 W cm−2 power density), in accordance with the protocol for advanced oxidation catalysts in published work (DOI: 10.1039/D4NR02819H). The S3 sample with the optimal photocatalytic performance was selected as the test object, and the standard operation procedure for each cycle was strictly unified to ensure the comparability of the test results.
3.5.1 Experimental procedure for reusability tests. (1) First cycle reaction: the S3 catalyst was added to an MO solution (pH = 2) for NIR-driven photocatalytic degradation, and the MO decolorization efficiency was determined after 7 h of irradiation according to the method in Section 3.3.1.

(2) Catalyst recovery and regeneration: after each cycle of reaction, the catalyst was rapidly separated from the reaction system by high-speed centrifugation (8000 rpm, 10 min), then thoroughly washed with deionized water and anhydrous ethanol, alternately, 3 times to remove the MO molecules and reaction byproducts adsorbed on the catalyst surface, and finally dried in an air-drying oven at 80 °C to a constant weight to ensure complete removal of the surface impurities.

(3) Subsequent cycles: the regenerated catalyst was reintroduced into fresh MO solution to carry out the next round of photocatalytic degradation reaction under identical experimental conditions. The above steps were repeated for a total of five consecutive cycles, and the MO decolorization efficiency of each cycle was recorded and calculated.

3.5.2 Results and analysis of five-cycle reusability tests. The MO decolorization efficiency of the S3 sample in five consecutive photocatalytic degradation cycles is shown in Fig. 12, and the key performance data are summarized in Table 3. It can be clearly observed from the test results that the NaYF4:Yb3+,Tm3+@TiO2 composite photocatalyst maintains excellent catalytic activity and stability during five consecutive cycles. The MO decolorization efficiency remains above 94% even after the 5th cycle, and the relative retention rate of catalytic activity is still as high as 95% compared with the 1st cycle, showing no significant decline in performance. The slight decrease in catalytic activity (about 4.2% in total after five cycles) is mainly attributed to the minor loss of catalyst powder during the centrifugation, washing and transfer processes, rather than the structural damage or deactivation of the catalyst itself. No obvious agglomeration or structural collapse of the catalyst was observed during the test, which is consistent with the excellent phase and surface chemical stability verified by the post-reaction XRD characterizations.
Table 3 MO decolorization efficiency of the S3 sample in five consecutive NIR photocatalytic cycles (7 h irradiation and pH = 2)
Cycle number Decolorization efficiency Relative retention rate of the catalytic activity (vs. 1st cycle)
1st 98.2% 100.0%
2nd 97.5% 99.3%
3rd 96.8% 98.6%
4th 95.4% 97.1%
5th 94.1% 95.8%


To further verify the structural durability of the catalyst after long-term cyclic use, Fig. 11 presents the upconversion luminescence (UCL) spectra of the fresh NaYF4:Yb3+,Tm3+ microrods, the fresh S3 sample, and the S3 sample after the 5th cycle, all measured under 980 nm laser excitation. Notably, all the characteristic upconversion emission peaks of Tm3+ ions (e.g., 450 nm, 475 nm, and 650 nm) in the 5th-cycle S3 sample are well retained, with no significant shift in peak positions relative to the fresh sample. The relative intensities of these emission peaks also remain nearly unchanged, demonstrating that the upconversion luminescence performance of the NaYF4:Yb3+,Tm3+ core, which is critical for NIR light harvesting and efficient energy transfer to the TiO2 shell, is fully preserved after prolonged cyclic use. This result further confirms that the core–shell structure of the NaYF4:Yb3+,Tm3+@TiO2 composite remains structurally intact, and the optical properties essential for photocatalytic activity are stably maintained, providing robust evidence for the excellent long-term structural durability of the catalyst in repeated applications (Fig. 12).


image file: d6ra00088f-f11.tif
Fig. 11 XRD patterns of the NaYF4:Yb3+,Tm3+ microrods and the S3 sample after five cycles of photocatalytic reaction. Note: fresh = before photocatalytic reaction and post-reaction = after 12 h of NIR-driven MO degradation (pH = 2), washed and dried.

image file: d6ra00088f-f12.tif
Fig. 12 Upconversion luminescence spectra of the NaYF4:Yb3+,Tm3+ microrods and S3 sample after the 5th cycle compared with the fresh sample under a 980 nm laser excitation. Note: fresh = before photocatalytic reaction.

4. Photocatalytic mechanism of NaYF4:Yb3+,Tm3+@TiO2 composites

Fig. 13 illustrates the energy level diagrams of Yb3+–Tm3+ and the upconversion luminescence processes in an Yb3+–Tm3+ co-doped system upon 980 nm NIR excitation, as well as the energy transfer and photocatalytic degradation mechanism of the NaYF4:Yb3+,Tm3+@TiO2 composite catalyst. The 980 nm NIR pump light only excites the Yb3+ ions (2F7/22F5/2) and three successive energy transfers from Yb3+ to Tm3+ populate the 3H5, 3F2, and 1G4 levels. The 1D2 level of Tm3+ cannot be populated directly by the fourth photon from Yb3+ via energy transfer due to the large energy mismatch (about 3500 cm−1) between them, and the cross-relaxation between Tm3+ ions is responsible for populating the 1D2 level. Usually, there are primarily two cross-relaxation processes that populate the 1D2 level: 3F2 + 3H43H6 + 1D2, and 1G4 +3H43F4 + 1D2. In addition, the 1D2 state can be promoted to the 3P2 state via another energy transfer from excited Yb3+ and then relaxes non-radiatively to the 1I6 level.
image file: d6ra00088f-f13.tif
Fig. 13 Energy level diagram of Yb3+–Tm3+ and the upconversion luminescence processes in an Yb3+–Tm3+ co-doped system under 980 nm excitation.

In the NaYF4:Yb3+,Tm3+@TiO2 composite system, the energies of the 1I6 and 1D2 levels of the Tm3+ ions are greater than the bandgap width of TiO2 (3.2 eV). The Tm3+ ions at these two energy levels (1I6 and 1D2) can directly and effectively transfer energy to the surrounding TiO2 through the fluorescence resonance energy transfer (FRET) process, which is the core mechanism for enhancing the NIR-driven photocatalytic activity of the composite catalyst. When TiO2 in the composite material is activated by the transferred energy, the electrons in the valence band (VB) transition to the conduction band (CB) and become photogenerated electrons (e), leaving photogenerated holes (h+) in the valence band at the same time.

Part of the photogenerated electron–hole pairs recombine either inside the material or after migrating to the surface, releasing energy in the form of heat. Another part migrates from the interior of the semiconductor to its surface to participate in the corresponding redox reactions: the excited electrons that migrate to the surface of TiO2 react with the oxygen molecules (O2) or H+ adsorbed on its surface to generate O2 or O22− and hydrogen peroxide (H2O2). H2O2 can react with superoxide anion radicals to produce hydroxyl radicals (˙OH). Meanwhile, the photogenerated holes react with H2O to generate hydroxyl radicals (˙OH). The generated hydroxyl radicals (˙OH) have strong oxidizing properties and are extremely reactive. The chemical reactions in which they participate proceed at a very rapid rate and belong to free radical reactions. ˙OH rapidly breaks the N–N and C–C bonds in the molecular structure of MO adsorbed on the surface of TiO2 particles, generating inorganic small molecular substances, thus achieving the purpose of degrading organic dye molecules.

In addition, the 1G4 energy level of Tm3+ ions has a lower energy than the bandgap width of TiO2, and thus no energy transfer occurs between this energy level and TiO2, which is consistent with the result that the blue-light upconversion luminescence intensity of the composite material remains almost unchanged after TiO2 coating.

5. Conclusion

This study provides a feasible preparation method for NaYF4:Yb3+,Tm3+-based upconversion@TiO2 core–shell composite photocatalysts and clearly clarifies their intrinsic energy transfer mechanism under NIR-driven photocatalytic performance. The as-prepared NaYF4:Yb3+,Tm3+@TiO2 microrod composites integrate excellent NIR photocatalytic activity, robust structural and chemical stability, and favorable reusability, which endows them with great practical application potential in solar-driven organic dye wastewater treatment. Beyond the material preparation and performance validation, this work also reveals the core role of fluorescence resonance energy transfer (FRET) between the NaYF4:Yb3+,Tm3+ upconversion core and anatase TiO2 shell in enhancing NIR photocatalysis, verifying that energy transfer from the Tm3+ excited states to TiO2 efficiently generates photogenerated electron–hole pairs and subsequent ˙OH radicals for pollutant degradation. The systematic investigation of pH-dependent photocatalytic performance also provides clear guidance for the practical application of the composite catalyst in actual wastewater systems with varying acid–base properties. In summary, this research not only develops a high-performance NIR-responsive photocatalyst for environmental remediation but also provides valuable theoretical and experimental insights for the rational design and fabrication of advanced upconversion-based composite photocatalysts, laying a solid foundation for the further development of solar light-driven photocatalytic technologies for water pollution control.

Conflicts of interest

There are no conflicts to declare.

Data availability

All data supporting the findings of this study, including structural, optical and photocatalytic data, are available in the article and Supplementary Information (SI). Supplementray information is available. See DOI: https://doi.org/10.1039/d6ra00088f.

Acknowledgements

The authors would like to thank Ningbo Key Laboratory of Intelligent Medical Chip and Equipment Technology and the “Five Categories of Projects” Program for Educational Reform through Industry-Education Integration in Ningbo (2024) for funding.

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