Skip to main content

Understanding the Structural-Dependent Photocatalytic Antibacterial Activity: a Case Study of Ag Modified BiVO4


In this work, Ag/BiVO4 heterostructural photocatalysts were developed in order to reveal exceptional structural-dependent photoinduced charge migration kinetics as well as the underlying photocatalytic antibacterial dynamic process. The structure-dependent interface of BiVO4 and Ag nanoparticles was successfully constructed to improve the photoinduced interface charge transfer efficiency and interface correlation. DFT calculation indicated that a net charge of about 0.33 e between Ag and tz-BiVO4 was achieved by extraordinary interface charge transfer, being far larger than that between Ag and ms-BiVO4. Larger net charge has consequences on mobility of charge carriers of tz-BiVO4 that can raise the migration and separation of charge carriers for Ag/tz-BiVO4 heterojunction. Fine interfacial contact between Ag and tz-BiVO4 led to the optimized photocatalytic performance toward E. coli inactivation, being predominately higher than that of tz-BiVO4, ms-BiVO4, and Ag/ms-BiVO4 catalysts. Besides photocatalytic activity, the thermocatalytic inactivation activity of Ag/tz-BiVO4 also exhibited a factor of about 7.2 and 3.1 times higher than that of tz-BiVO4 and Ag/ms-BiVO4. Trapping and EPR measurements suggested that the structural-dependent photocatalytic activity of Ag/BiVO4 mainly originated from the pronounced variation of the capability to produce H2O2 active species, where the capability of generating H2O2 over Ag/tz-BiVO4 is highly accelerated. Moreover, it cannot be ignored that this study provides an ideal candidate for many aspects, such as environmental and water pollution caused by pathogenic microorganisms and disinfection of medical materials, food packaging, household materials, and public places, etc.


Utilization of solar light and semiconductors for photocatalytic purpose is still a research hotspot, which is found wide applications in energy conversion and environmental remediation [1, 2]. Nano-heterojunctions have also received attention that has to be taken seriously, because they can be applied to various aspects and have achieved extraordinary results in many potential applications [3,4,5,6,7,8]. Furthermore, due to its advantages of high efficiency, environmentally friendly, and renewable energy, photocatalytic antibacterial technology has an irreplaceable role in environmental governance and sterilization [9, 10]. Recently, BiVO4 emerges an excellent candidate because of its tunable crystal structure and appropriate electronic structure [11, 12]. However, despite the favorable structural characteristics of BiVO4, inefficient charge carrier transmission and short length of carrier diffusion are hindrance of its application in practice. From solid state physics viewpoint, the photocatalytic performance is thought to be predominately regulated by the distortion of microstructure. The tetragonal zircon (tz-) BiVO4 synthesized by ethylene-glycol colloidal path controllable at room temperature induces strongly improved photocatalytic activity over monoclinic scheelite (ms-) BiVO4, yet the underlying mechanism remains ambiguous [13]. Therefore, the modification of BiVO4 is not limited to improving the photocatalytic activity; it is also absolutely necessary to explain the kinetics of photoinduced charge transfer from the microstructure.

Frequently, localizations of excess charge carriers as the so-called localized polarons accompanied by microstructural and interfacial regulation have intensely emotional impact on charge carrier mobility of oxide semiconductors. Localized polarons in BiVO4 either inhibit the kinetics of charge mobility or influence the photocatalytic activity at surfaces [14, 15]. The reconstruction of surface or interface structures can drive the variation of polaron extension that affects the mobility of charge carriers as well as the photocatalytic performance. Noble metals, like Ag, Au, and et al., can act as photosensitizers to absorb visible light and regulate the generation of charge carrier through direct electron transfer or dipole-dipole coupling connection [16, 17]. The junction of noble metal with semiconductor to establish interfacial charge transfer provides an efficient approach to influence the polaron extension as well as the mobility of charge carriers that can raise the migration and separation of charge carriers. For instance, Au nanosphere decorated Mo:BiVO4 photoanode displays increased photocurrent intensity of about 2.2 times in comparison to Mo:BiVO4 [18]. Recent investigations on Ag/BiVO4 nanostructures demonstrate highly improved photocatalytic performance toward water oxidation, organic dye degradation, and so forth [19, 20]. Most reports very often merely concentrated on fine characterization of photocatalytic response but did not focus on the microstructural analyses which profoundly governed the native photophysical and photochemical performance of semiconductors. Considering to uncovering the structural-dependent native properties, experimental identification of phase structure as well as surface/interface feature of Ag/BiVO4 nanostructure is essential and advantageous to regulate the native properties and provides some hints to various structural-linked semiconductors.

Herein, this work means to deliver a proof by rationally controlling the phase structure of BiVO4 and assembling Ag nanoparticles for photocatalytic antibacterial purpose in order to reveal structural-dependent photoinduced charge migration as well as the underlying photocatalytic antibacterial dynamic process.



Bismuth nitrate (Bi(NO3)3•5H2O) (purity 99%), silver nitrate (AgNO3) (purity 99.8%), and absolute ethanol (purity 99.7%) were obtained from Wind ship in Tianjin chemical reagent Co. Ltd (Tianjin, China). Ammonium metavanadate (NH4VO3) (purity 99.9%) was purchased from Adamas Reagent Co. Ltd (Shanghai, China). Distilled water was also needed. All reagents were used without further purification.

Synthesis of BiVO4 and Ag-Loaded BiVO4

Synthesis of BiVO4

BiVO4 samples were prepared by hydrothermal method. One millimole of Bi(NO3)3 was added into 20 mL of distilled water under mild stirring, and a white suspension was formed for 30 min. One millimole of NH4VO3 was added into 40 mL of distilled water to form a white suspension with stirring for 30 min. Then, NH4VO3 suspension was dropwised into the Bi(NO3)3 solution to form an orange suspension. The pH value of the orange suspension is 0.59. Sodium hydroxide solution was adopted to adjust the pH value from 0 to 12 for the above suspension. And the suspension was loaded into a 100 Teflon-lined autoclave. The autoclave was sealed and heated in an oven at 180 °C for 12 h. The pH value of the suspension after the reaction was maintained. The autoclave was then naturally cooled to room temperature, where the obtained yellow powder was collected and washed with distilled water and ethanol several times to remove ions and possible remnants until the pH value near neutral and vacuum-dried for further characterization.

Synthesis of Ag-Loaded BiVO4

A set of five identical solutions was prepared, each of which contains 1 g BiVO4 mixed in 40 mL of ethanol and sonicated for 10 min. Another set of solutions containing an appropriate amount of AgNO3 was obtained. Then, AgNO3 aqueous solution was carefully dropped into BiVO4 solution and kept in the dark for 1 h with constant stirring. After that, the mixture of AgNO3 and BiVO4 was exposed to UV light for 2 h with stirring so as to Ag nanoparticles loaded BiVO4 samples. The samples were then dried overnight at 60 °C. The initial Ag loading content was fixed to be 1 wt%, 3 wt%, 5 wt%, 7 wt%, and 10 wt%.

Bacteria Preparation

The lyophilized powder was dissolved, and 1 mL of the bacterial suspension was adhered to the solid culture plate with a hot-sterilized toothpick. The inoculated solid culture plate was inverted and placed in a 37 °C incubator for 12 h. Then, the selection of the single colony and the expansion of the culture are carried out. The final cell density was adjusted to about 1 × 107–1 × 109 colony forming unit (CFU) mL−1.

Photocatalytic Bacterial Inactivation

The VLD photocatalytic inactivation of Escherichia coli (E. coli ATCC 8099, Gram-negative bacteria) and Staphylococcus aureus (S. aureus ATCC 25923, Gram-positive bacteria) by Ag/tz-BiVO4 was conducted under fluorescent tubes (PCX50C Discover) irradiation. A suspension (40 mL) containing the bacterial cells and the photocatalyst (40 mg). Then, the solution was turned on to start the photocatalytic inactivation experiments. At different time intervals, aliquots of the samples were collected and serially diluted with sterilized aqueous solution. Then, 1 mL of the diluted samples was immediately spread on Nutrient Agar plates and incubated at 37 °C for 12 h to determine the number of survival cells. S. aureus cultured at 54 °C for 24 h. For the comparison, light control (bacterial cells and light without photocatalyst) and dark control (photocatalyst and bacterial cells without light) were also conducted in the study.

The photocatalytic degradation performance of the prepared samples was evaluated by photodegradation of the MB (Methylene Blue) dye solution (5 mg/L, 30 mL) under visible light irradiation. A 300 W Xenon lamp equipped with a 420-nm cutoff filter was used as the light source. In the photodegradation experiment, 15 mg of photocatalysts was dispersed in 30 mL of the MB dye solution. To ensure the balance of adsorption and desorption, the quartz tube containing the solution was kept in the dark for 1 h before irradiation. At specific time intervals, 4 mL of the suspension was collected and analyzed by UV-visible diffuse reflectance spectrometer. The absorption peaks at 672 nm were employed to determine the concentration of the residual MB solution.

To identify the dominant reactive species accounting for the photocatalytic bacterial inactivation, specific compounds (i.e., respective scavengers) at predetermined optimized concentration were individually added into reaction solution with identical conditions mentioned above. All the above experiments were repeated in triplicates. At the same time, the capture experiment of photocatalytic degradation of MB solution was also performed.

Preparation Procedure for SEM Observation of Bacteria

The mixtures of photocatalyst E. coli before and after the inactivation were firstly sampled and centrifuged and wash the bacteria solution twice with PBS (phosphate buffer saline). After this, the harvested cells were prefixed in 2.5% glutaraldehyde for 12 h. After washed with 0.1 M PBS, the specimens were dehydrated in a graded series of ethanol (20% for once, 50% for once, 80% for one time, 100% for one time) each for 10 min and then wash the sides with t-butanol. Finally, drop it onto a clean silicon wafer for SEM observation.

Morphology, Structure, and Optical Properties Characterizations

Phase purity of all samples was characterized by X-ray diffraction (XRD) on Rigaku DMAX2500 X-ray diffractometer using a copper target (λ = 0.15406 nm). The scanning speed was 1° per minute, the scanning step was 0.05°, and the scanning range was set to 5–80°. Morphology of the samples was determined using scanning electron microscopy (SEM) on S4800 apparatus working at 10 kV and transmission electron microscopy (TEM) on a DHG-9240B FEI apparatus with an acceleration voltage of 200 kV. Appropriate amount of catalyst to be tested was dispersed it in absolute ethanol by ultrasonic dispersion. In the SEM test, the dispersed sample was dropped on a clean silicon wafer, and in the TEM test, it was dropped on a copper mesh supported by a carbon film. X-ray photoelectron spectroscopy (XPS) measurement were performed on a Thermo ESCALAB 250 with Al Ka (1486.6 eV) line at 150 W. To compensate for surface charges effects, the binding energies were calibrated using the C 1 s peak at 284.60 eV as the reference; the casaXPS program was used to realize the quantification of the elements. UV-visible diffuse spectra of the samples were measured using Lambda 750 s UV/vis spectrometer. Barium sulfate was chosen as the reference substrate, and the scanning test range was set to 200~800 nm. Surface photovoltage spectrum (SPV) was obtained by a self-assembly system consisting of a sample chamber, a lock-in amplifier with a light chopper, and a 300 W Xenon lamp as light source. The photoelectrochemical performance of the samples was recorded on AUT302N electrochemical workstation (Metrohm) with standard three-electrode cell. Among them, the electrodes of catalyst sample, standard Ag/AgCl, and platinum were defined as the electrode of working, reference, and counter, respectively. The electrolyte solution was sodium sulfate (Na2SO4) solution with the concentration of 0.2 M, and the light source was LED light. Photoluminescence spectra analysis was carried out on an Edinburgh Instruments FLS920 spectrofluorimeter. Electron Paramagnetic Resonance (EPR) spectra for hydroxyl radicals (sample, 4 mg; DMPO, 0.22 M; aqueous solution volume, 2.0 mL) and superoxide radicals (sample, 4 mg; DMPO, 0.22 M; methanol solution volume, 2.0 mL) were provided both in dark and visible light irradiation at 3186 G and 9056.895 MHz by an ER200-SRC electron spin resonance spectrometer (Bruker, Germany). The magnetic field strength, microwave strength, and scan width were set to 0.2 mT, 1 mW, and 250 mT, respectively. The sample to be tested was placed inside the NMR tube, and the test was performed in air at room temperature. All structural optimization and property calculations were performed using the CASTEP program package based on density functional theory (DFT) in the Materials Studio 2017 R2. The Perdew Burke Ernzerh (PBE) of generalized gradient approximation (GGA) was selected for exchange correlation of the interaction between electrons. The kinetic cut-off energy of 380 eV was set. The plane wave function was used as basis sets. The calculations of the electronic state and state density were performed based on the optimized crystal structure.

Results and Discussion

XRD data imply that a phase structure variation from monoclinic scheelite (ms-) to tetragonal zircon (tz-) structure of BiVO4 can be achieved (Fig. S1). The junction of Ag nanoparticles led to no obvious alteration of the diffraction peaks of BiVO4 (Fig. 1a and Fig. S2). However, from Rietveld’s refined results, it is noted that either Ag/tz-BiVO4 or Ag/ms-BiVO4 showed an apparent lattice expansion in comparison to pristine tz-BiVO4 and ms-BiVO4 samples, which is summarized in Table S1. Lattice variation of BiVO4 matrix promised fine interfacial contact between Ag and BiVO4 nanoparticles, which is also proved by TEM observations. TEM and HRTEM images were given in Fig. 1b. Apparently, either ms-BiVO4 or tz-BiVO4 can act as a support to bind highly dispersed Ag nanoparticles, where the content of Ag nanoparticles is close to initial value as verified by EDS data (Fig. S3) [21, 22]. The d-spacing of 0.239 nm corresponds to the (111) plane of Ag (JCPDS No. 87-0597), whereas the adjacent lattice fringes of 0.308 nm and 0.484 nm are closely related to the (112) plane of ms-BiVO4 and (200) plane of tz-BiVO4, respectively.

Fig. 1

a XRD patterns of pristine tz-BiVO4, Ag/tz-BiVO4 sample, pristine ms-BiVO4, and Ag/ms-BiVO4 sample. b TEM image of Ag/tz-BiVO4, HRTEM of Ag/tz-BiVO4, TEM image of Ag/ms-BiVO4, and HRTEM of Ag/ms-BiVO4

To acquire the surface chemical composition and oxidation states of the as-prepared samples, XPS technique was adopted. XPS results can fully verified that the Ag/BiVO4 catalyst was successfully prepared by the analyses of the binding energies over Bi, V, O, and Ag elements, as illustrated in Fig. 2 and Fig. S4. From Fig. 2a, it is seen that the Bi 4f orbital of tz-BiVO4 can be well-reproduced to two peaks with binding energies of 164.1 eV and 158.8 eV, which can be ascribed to the Bi 4f5/2 and Bi 4f7/2 orbitals, being close to the previous reported value [23, 24]. As for Ag/tz-BiVO4, a slight toward lower binding energy of about 0.3 eV was observed for Bi 4f orbital. Figure 2 b shows the high-resolution XPS data of V element. It is clearly that the binding energies of V 2p1/2 and V 2p3/2 locate at ~ 524.2 eV and 516.6 eV for pristine tz-BiVO4. Similar to that of Bi 4f orbital, V 2p orbital also gave a red shift of the binding energies for Ag/tz-BiVO4 heterojunction. Moreover, the O 1 s XPS analysis was also illustrated in Fig. 2c. Three typical binding energies of O 1 s orbital for tz-BiVO4 appears at 529.6 eV, 531.6 eV, and 533 eV, respectively, which can be assigned to the lattice oxygen, oxygen of surface hydration as well as the chemical-absorbed molecular O2, respectively [25]. As for Ag/tz-BiVO4, a red shift of ~ 0.2 eV was observed for the lattice oxygen in comparison to pristine tz-BiVO4. Such a behavior is supposed to be related to lattice expansion as well as the interfacial interaction between Ag and tz-BiVO4. Very often, the lattice expansion accompanies with elongated average lattice bonds and weakened strength of these bonds, which leads to the decrease of binding energies [26]. On the other hand, the variation of binding energies reflects the rearrangement of electron density near atoms, which can be influenced by surface modification. The decrease of the binding energies also implies the fine interfacial contact between Ag and tz-BiVO4, predicting an interfacial transfer may occur, which resulted in the variation of electron density [27]. This suspension can be verified by the following theoretical results. Moreover, XPS data also confirmed the metallic feature of Ag nanoparticles, and no evidence of Ag+ was observed in Ag/tz-BiVO4 heterojunction (Fig. 2d) [28]. On the other hand, the XPS results of Ag/ms-BiVO4 were also given in Fig. S4. Similar to that of Ag/tz-BiVO4 heterojunction, the binding energies of Bi 4f, V 2p, and O 1 s orbitals in Ag/ms-BiVO4 also exhibited a tiny redshift of about 0.1~0.2 eV. The slight variation of the binding energy shift in Ag/tz-BiVO4 and Ag/ms-BiVO4 is likely to be ascribed to the structural-dependent interfacial feature of BiVO4 and Ag nanoparticles.

Fig. 2

XPS spectra of tz-BiVO4 and Ag/tz-BiVO4 samples: (a) Bi 4f, (b) V 2p, (c) O 1 s, and (d) Ag 3d orbital

Since the lattice expansion of BiVO4 occurred after Ag modification, the electronic structure may also be influenced, which can be verified by density functional theory (DFT) calculations. Because of large lattice mismatch between Ag and BiVO4, the convergence and structural optimization of Ag/BiVO4 is inaccessible. Thereby, a cluster/surface model was established to reveal the interfacial correlations between Ag and BiVO4 (Fig. S5 and Fig. S6). The band gap energy of tz-BiVO4 was estimated to be 2.59 eV, which is larger than that of 2.17 eV for ms-BiVO4 (Fig. S7), being in accordance to previous reported results [13, 29]. The anchoring of Ag cluster on BiVO4 surfaces has no obvious consequences on the typical electronic transitions from O 2p to V 3d orbital, as illustrated by the UV-visible diffuse reflectance spectra of the as-prepared samples (Fig. 3a). From Fig. 3a, it is seen that both ms-BiVO4 and tz-BiVO4 showed visible light response. According to Kubelka-Munk theory, the band gap energy of the samples can be calculated from the relationship between light absorption and band gap.

Fig. 3

UV-visible diffuse reflectance spectra (a) and surface photovoltage spectra (b) of the as-prepared samples

(αhν)2= A(hν − Eg)

where α, h, ν, Eg, and A mean absorption rate, Planck constant, frequency, band gap, and constant, respectively. The band gap energy of ms-BiVO4 and tz-BiVO4 was estimated to be 2.40 eV and 2.69 eV, respectively (Fig. S8), being close to the DFT results. It is noted the modification of Ag nanoparticles on BiVO4 surfaces led to an extension of the visible light absorption (Fig. S9). The broadened absorption should be originated to the SPR effects of Ag nanoparticles. Besides visible light absorption capability, the modification of Ag nanoparticle on BiVO4 can also has great impact on the kinetics of photoinduced charge carriers.

As illustrated by the surface photovoltage (SPV) signals in Fig. 3b, the maximal SPV signal of tz-BiVO4 was achieved to 0.33 mV after Ag modification, which is about 91.7 times higher than that of pristine tz-BiVO4. Moreover, it is noted that the intensity of SPV signal for Ag/tz-BiVO4 is also much higher than that of Ag/ms-BiVO4. Frequently, the SPV signal derived only from the photoinduced charge generation and separation process so that the intensity of the SPV signal reflects the efficiency of the charge carrier separation [30, 31]. Higher signals often predict improved charge separation efficiency, which suggests that stronger interaction between Ag and tz-BiVO4 exists than that for Ag and ms-BiVO4, being further clarified by DFT calculations. The atomic population analysis suggests that tz-BiVO4 acquired a net charge of about 0.33 e after Ag cluster modification. While for ms-BiVO4, only a small net charge of ~ 0.04 e occurs when anchored with Ag cluster (Table S2). Since the interfacial charge transfer highly depends on the Fermi levels as well as the electronic structures. To confirm the atomic population and the charge isolation between Ag and BiVO4, the work functions of BiVO4 and Ag/BiVO4 were given in Fig. 4. As illustrated in Fig. 4 a and b, the work functions for tz-BiVO4 and ms-BiVO4 were calculated to be 4.569 eV and 5.621 eV through aligning Fermi level to vacuum energy level (EVL). On the basis of the relationship between EVL and normal hydrogen electrode (NHE) [32], the Fermi levels of tz-BiVO4 and ms-BiVO4 were determined to be 0.069 V and 1.121 V, respectively. In view of solid-state physics, electrons can flow between hetero-interfaces, being highly dependent on the location of Fermi levels. Since the Fermi level of Ag locates at 0.4 V vs NHE, which is higher than that of tz-BiVO4 so that electrons will transfer from tz-BiVO4 surfaces to Ag. As a consequence, Ag is negatively charged, and tz-BiVO4 is positively charged, being in accordance to DFT results. This result predicts an internal electric field directed from Ag to tz-BiVO4, suggesting an efficient injection of photoinduced electrons from the conduction band of tz-BiVO4 to Ag would occur. As for ms-BiVO4, its lower Fermi level expects an inverse electron transfer process from Ag to ms-BiVO4. However, atomic population analysis demonstrated that no apparent electron migration between Ag and ms-BiVO4 was observed. This outcome may imply poor photoinduced charge carrier separation efficiency for Ag/ms-BiVO4 heterocatalyst.

Fig. 4

The work function of pristine tz-BiVO4 (a) and pristine ms-BiVO4 (b)

Having the above-mentioned results in mind, Ag/BiVO4 heterostructures would display structural-dependent photocatalytic performance. A wild bacterium, E. coli, was chosen as a model bacterium to study the photocatalytic inactivation activity of Ag/tz-BiVO4 and Ag/ms-BiVO4, respectively. Because E. coli is a Gram-negative bacterium, an auxiliary study was also carried out using a representative of Gram-positive bacteria with S. aureus (Fig. S10). A comparative study was firstly conducted to verify the inactivity of visible light toward the E. coli inactivation. As shown in Fig. 5a, the inactivation experiments of E. coli by tz-BiVO4, Ag/tz-BiVO4, ms-BiVO4, and Ag/ms-BiVO4 were carried out under visible light irradiation. It can be seen from Fig. 5a that the inactivation performance for E. coli over pristine tz-BiVO4 and ms-BiVO4 photocatalyst was merely detectable. However, anchoring of Ag nanoparticles can modulate the photocatalytic inactivation performance of BiVO4 (Fig. S11). Meanwhile, a structural-dependent photocatalytic performance was observed. When the weight ratio of Ag reached to 7%, Ag/tz-BiVO4 exhibited optimized photocatalytic inactivation efficiency over E. coli compared with some materials in the previous reports (Table S3). Within 90 min, the efficiency of bacterial inactivation reaches 100%, whereas Ag/ms-BiVO4 hetero-photocatalyst displayed tiny photocatalytic activity toward E. coli inactivation under VL irradiation (Fig. S11). As reported previously, Ag nanoparticles have found to show antibacterial activity. Thereby, a controlled experiment was carried in a dark chamber to testify the synergy of photocatalytic effect of Ag/BiVO4 heterostructures for the inactivation of E. coli. As shown in Fig. 5b, the inactivation process was conducted within 2 h under VL irradiation or in dark to compare photocatalytic and thermocatalytic sterilization effect of the as-prepared catalysts. It is found that ms-BiVO4 was inert to the inactivation of E. coli, while tz-BiVO4 exhibited poor activity either under VL irradiation or in dark. After Ag nanoparticles modification, the thermocatalytic activity was greatly improved. For instance, the thermocatalytic inactivation activity of Ag/tz-BiVO4 improved a factor of about 7.2 and 3.1 times higher than that of tz-BiVO4 and Ag/ms-BiVO4. Moreover, with VL irradiation, the catalytic activity of both Ag/tz-BiVO4 and Ag/ms-BiVO4 was predominately enhanced. The similar results can be obtained in the photocatalytic degradation of MB dye solution (Fig. S12a). After 7 h of visible light irradiation, the photocatalytic degradation rate of MB dye solution by 7Ag/tz-BiVO4 can reach about 85%. So as to know the destruction process of E. coli by Ag/tz-BiVO4, SEM observation was conducted to examine the morphology changes during the photocatalytic inactivation process as illustrated in Fig. 5 c and d. As shown in Fig. 5c, when the bacterial was not in contact with the catalyst, E. coli exhibited a well-preserved rod shape and intact cell structure. After 2 h irradiation reaction, disorganized membrane structures are observed (Fig. 5d), which demonstrates that the cell is completely decomposed. This matches well with the previous studies that photocatalytic treatment can induce significant disorder in membrane permeability of bacterial cells.

Fig. 5

Photocatalytic inactivation of E. coli by Ag/tz-BiVO4 and Ag/ms-BiVO4 photocatalysts under VL irradiation (a). Comparison study of photocatalytic and thermocatalytic sterilization effect (b). SEM images of individual E. coli cell being photocatalytically inactivated by Ag/tz-BiVO4 for 0 h (c) and 2 h (d)

To get further information of the photocatalytic process as well as the radical oxygen species that determine the inactivation process of E. coli, several types of radical species scavengers were carefully introduced by repeating the photocatalytic process of E. coli inactivation. As shown in Fig. 6a, sodium oxalate, isopropanol, Cr(VI), Fe(II)-EDTA, and Tetramethylpiperidine (TEMPOL) were taken as the scavengers for holes (h+), hydroxyl radicals (•OH), electrons (e), H2O2, and superoxide radicals (•O2) [33, 34]. Before the scavenger experiment was performed, the concentrations of different scavengers were optimized in earlier research. When no scavenger was added, 106 cfu mL−1 of E. coli could be completely inactivated within 90 min. The bacterial inactivation is virtually suppressed with the addition of TEMPOL and Fe(II)-EDTA as the scavenger of •O2 and H2O2, suggesting that •O2 and H2O2 played critical roles in the photocatalytic inactivation process. After the addition of sodium oxalate and isopropanol, it can be observed that the bactericidal inactivation efficiency over Ag/tz-BiVO4 were partially inhibited, suggesting that h+ and •OH could directly destroy the E. coli cells with a powerful oxidation capability, whereas photoinduced electrons exhibited unobservable impact on the inactivation process of E. coli. And the capture experiment of photocatalytic degradation of MB dye solution was also carried out under visible light irradiation. In Fig. S12b, t-BuOH, silver nitrate (AgNO3), ethylenediaminetetraacetic acid (EDTA), and Fe(II)-EDTA were taken as the scavengers for •OH, e, h+, and H2O2, respectively. The results indicate that H2O2 is the main active species in the experiment of photocatalytic degradation of MB dye solution. The active species •OH, e, and h+ also have different effects on the photocatalytic degradation process, which is different from the role of active species in the photocatalytic sterilization capture experiment caused by errors in the plate counting method.

Fig. 6

Photocatalytic inactivation efficiencies with respective scavengers in the presence of Ag/tz-BiVO4 (a). EPR spectra of •OH and DMPO-•O2 in the presence of pristine tz-BiVO4, Ag/tz-BiVO4, pristine ms-BiVO4, and Ag/ms-BiVO4 under VL irradiation (b). Relative concentration of H2O2 by pristine tz-BiVO4, Ag/tz-BiVO4, pristine ms-BiVO4, and Ag/ms-BiVO4 (the pH of the suspension was adjusted to 9 using NaOH and took 3.5 mL; 50 μL of 0.7 mM lucigenin solution was added) (c)

To acquire further information of the active species, electron paramagnetic resonance (EPR) measurement was used. In brief, DMPO acted as a spin trapper to testify the existence of •O2 and •OH species [35, 36]. As displayed in Fig. 6b, very weak characteristic EPR signal of DMPO-•OH species was observed by prolonging VL irradiation time (Fig. S13). After Ag nanoparticles modification, the intensity of EPR signal of DMPO-•OH was drastically improved for both tz-BiVO4 and ms-BiVO4, suggesting that the capability to generate •OH for BiVO4 was greatly enhanced with Ag nanoparticles anchoring, being originated from the enhancement of charge carrier separation efficiency. Moreover, it is noted in Fig. 6c that the typical EPR signal of DMPO-•O2 was also detected for all as-prepared samples (Fig. S14). Similar result to the EPR signal of DMPO-•OH is that the intensity of DMPO-•O2 was also improved for Ag/tz-BiVO4 and Ag/ms-BiVO4 heterostructures. Interestingly, the EPR signal intensity of either DMPO-•OH or DMPO-•O2 for Ag/tz-BiVO4 is higher than that for Ag/ms-BiVO4. For photocatalytic process, the electronic band potential always plays dominate roles in modulating the active species as well as the photocatalytic activity. On the basis of Mulliken electronegativity and band gap energy [37], the conduction band potentials of tz-BiVO4 and ms-BiVO4 were calculated to be about 0.21 V and 0.30 V versus NHE (S15). Thereby, the valence band potentials tz-BiVO4 and ms-BiVO4 were determined to be 2.90 V and 2.70 V versus NHE. According to previous literatures, the redox potential of •OH/H2O locate at 2.38 V versus NHE [38], suggesting the participation of •OH in the photocatalytic process for the inactivation of E. coli. However, it is seen that the redox potential of •O2/O2 (− 0.33 V versus NHE) is more negative than the conduction potential of tz-BiVO4 and ms-BiVO4, indicating both tz-BiVO4 and ms-BiVO4 are not capable to generate •O2 reactive species. This result seems to be contrary to the trapping experiments. Then, it is necessary to specify the origination of the •O2 reactive species. In aqueous solution, a photoinduced hole can oxidize H2O2 to produce one •O2 via the following equation: H2O2 + h+ → •O2 + 2H+ [39]. Moreover, the generation •O2 can also be achieved by reaction of H2O2 with •OH by the following equation: H2O2 + •OH → •O2 + H2O + H+ [40]. From this point, the capability for the generation of H2O2 over the as-prepared BiVO4 samples should be investigated. The concentration of H2O2 as a function of VL irradiation time was given in Fig. 5c. Clearly, H2O2 can be generated for all as-prepared samples under VL irradiation. Predominantly, H2O2 concentration gradually increased from 6.40 to 30.69 μM in initial 120 min under VL irradiation for Ag/tz-BiVO4 heterostructure, which is much higher than the other samples. Consequently, junction of Ag and tz-BiVO4 can greatly improve the capability of the photocatalysts to generate H2O2 due to the fine interfacial contact, which resulted in highly improved photocatalytic activity toward E. coli inactivation as well as the phase dependent photocatalytic activity of Ag modified BiVO4 heterostructures.

As a result, a plausible explanation for the inactivation of E. coli over Ag/tz-BiVO4 was proposed. As the CB edge potential of tz-BiVO4 is higher than that of the metallic Ag nanoparticles, the electrons in the CB of tz-BiVO4 can quickly transfer toward to Ag nanoparticles, inhibiting the recombination of electron–hole pairs between the VB and CB of BiVO4. The photogenerated holes migrate to the surface of the semiconductor and then directly contact with bacteria, or even produce H2O2 and •OH with H2O molecules. Simultaneously, the enrichment of electrons on the Ag nanoparticles may be subsequently scavenged by H2O2 to produce •OH active species. The free radicals can react with the organic matter that constitutes the microbial organism and directly oxidize the organic matter into inorganic substances such as CO2 and H2O. This process will change the original state and properties of the microbial organism, thereby directly hindering the proliferation of microbial cells and preventing bacteria.


In summary, Ag/BiVO4 heterostructural photocatalysts were developed with the aim to deliver a proof by rationally controlling the phase structure of BiVO4 and assembling Ag nanoparticles for photocatalytic antibacterial purpose in order to reveal structural-dependent photoinduced charge migration as well as the underlying photocatalytic antibacterial dynamic process. DFT theoretical calculation indicates an interfacial charge transfer between Ag and tz-BiVO4 with a net charge of about 0.33 e, which is far larger than that between Ag and ms-BiVO4, predicting fine interfacial contact and improved charge separation efficiency of Ag/tz-BiVO4. Relying on further experimental characterization, the optimized photocatalytic performance toward E. coli inactivation of Ag/tz-BiVO4 is predominately higher than that of tz-BiVO4, ms-BiVO4, and Ag/ms-BiVO4 catalysts. Besides photocatalytic activity, the thermocatalytic inactivation activity of Ag/tz-BiVO4 also exhibited a factor of about 7.2 and 3.1 times higher than that of tz-BiVO4 and Ag/ms-BiVO4. In combination with trapping experiment and EPR measurement, •O2, •OH, and H2O2 active species played critical roles in the photocatalytic inactivation process. Moreover, detailed investigation suggested that the structural-dependent photocatalytic activity of Ag/BiVO4 mainly originated from the pronounced variation of the capability to produce H2O2 active species, where the capability of generating H2O2 over Ag/tz-BiVO4 is highly accelerated. This work provides hints for regulating the native properties of various structural-linked semiconductors.

Availability of Data and Materials

The datasets supporting the conclusions of this article are included within the article.



Scanning electron microscopy


Transmission electron microscopy


X-ray power diffraction


X-ray photoelectron spectroscopy


Electron paramagnetic resonance


Surface photovoltage spectrum


Density functional theory


  1. 1.

    Zou Y, Yang B, Liu Y, Ren Y, Ma J, Zhou X, Cheng X, Deng Y (2018) Controllable interface-induced co-assembly toward highly ordered mesoporous Pt@TiO2/g-C3N4 heterojunctions with enhanced photocatalytic performance. Adv. Funct. Mater 28:1806214–1806211

    Article  CAS  Google Scholar 

  2. 2.

    Yang C, Qin J, Xue Z, Ma M, Zhang X, Liu R (2017) Rational design of carbon-doped TiO2 modified g-C3N4 via in-situ heat treatment for drastically improved photocatalytic hydrogen with excellent photostability. Nano Energy 41:1–9

    Article  CAS  Google Scholar 

  3. 3.

    Haider M, Ijaz S, Ali J, Haider M, Imran H, Majeed I, Shahzadi MM, Ali JA, Khan MI (2020) Green synthesized phytochemically (Zingiber officinale and Allium sativum) reduced nickel oxide nanoparticles confirmed bactericidal and catalytic potential. Nanoscale Research Letters 15:50

    Article  CAS  Google Scholar 

  4. 4.

    Altaf S, Ajaz H, Imran M, Ul-Hamid A, Naz M, Aqeel M, Shahzadi A, Shahbaz A, Ikram M (2020) Synthesis and characterization of binary selenides of transition metals to investigate its photocatalytic, antimicrobial and anticancer efficacy. Appl Nanosci

  5. 5.

    Aqeel M, Ikram M, Asghar A, Haider A, Ul-Hamid A, Naz M, Imran M, Ali S (2020) Synthesis of capped Cr-doped ZnS nanoparticles with improved bactericidal and catalytic properties to treat polluted water. Applied Nanoscience 10:2045–2055

    Article  CAS  Google Scholar 

  6. 6.

    Haider M, Ijaz M, Imran M, Naz H, Majeed JA, Khan MM, Ali MI (2020) Enhanced bactericidal action and dye degradation of spicy roots’ extract-incorporated fine-tuned metal oxide nanoparticles. Applied Nanoscience 10:1095–1104

    Article  CAS  Google Scholar 

  7. 7.

    Ikram M, Abbasi S, Haider A, Naz S, Hamid Anwar UI, Imran M, Ghaffar A (2020) Bi-metallic Ag/Cu incorporated into chemically exfoliated MoS2 nanosheets to enhance antibacterial potential: insilico molecular docking studies. Nanotechnology

  8. 8.

    Wahab M, Imran M, Ikram M, Naz M, Aqeel A, Rafiq H, Majeed SA (2019) Dye degradation property of cobalt and manganese doped iron oxide nanoparticles. Applied Nanoscience 9:1823–1832

    Article  CAS  Google Scholar 

  9. 9.

    Wang W, Li G, Xia D, An T, Zhao H, Wong PK (2017) Photocatalytic nanomaterials for solar-driven bacterial inactivation: recent progress and challenges. Environmental Science-Nano 4:782–799

    Article  CAS  Google Scholar 

  10. 10.

    McEvoy JG, Zhang Z (2014) Antimicrobial and photocatalytic disinfection mechanisms in silver-modified photocatalysts under dark and light conditions. Journal of Photochemistry and Photobiology C-Photochemistry Reviews 19:62–75

    Article  CAS  Google Scholar 

  11. 11.

    Park Y, McDonald KJ, Choi KS (2013) Progress in bismuth vanadate photoanodes for use in solar water oxidation. Chem. Soc. Rev 42:2321–2337

    Article  CAS  Google Scholar 

  12. 12.

    Ordon K, Kassiba A, Makowska-Janusik M (2016) Electronic, optical and vibrational features of BiVO4 nanostructures investigated by first-principles calculations. RSC. Adv 6:110695–110705

    Article  CAS  Google Scholar 

  13. 13.

    Dolic SD, Jovanovic DJ, Smits K, Babic B, Marinovic-Cincovic M, Porobic S, Dramicanin MD (2018) A comparative study of photocatalytically active nanocrystalline tetragonal zyrcon-type and monoclinic scheelite-type bismuth vanadate. Ceram. Int 44:17953–17961

    Article  CAS  Google Scholar 

  14. 14.

    Kweon KE, Hwang GS, Kim J, Kim S, Kim S (2015) Electron small polarons and their transport in bismuth vanadate: a first principles study. Phys. Chem. Chem. Phys 17:256–260

    Article  CAS  Google Scholar 

  15. 15.

    Zhang L, Ye X, Boloor M, Poletayev A, Melosh NA, Chueh WC (2016) Significantly enhanced photocurrent for water oxidation in monolithic Mo:BiVO4/SnO2/Si by thermally increasing the minority carrier diffusion length. Energy Environ. Sci 9:044–2052

    Google Scholar 

  16. 16.

    Guo K, Liu Z, Han J, Zhang X, Li Y, Hong T, Zhou C (2015) Higher-efficiency photoelectrochemical electrodes of titanium dioxide-based nanoarrays sensitized simultaneously with plasmonic silver nanoparticles and multiple metal sulfides photosensitizers. J. Power Sources 285:185–194

    Article  CAS  Google Scholar 

  17. 17.

    Chen D, Liu Z, Guo Z, Yan W, Xin Y (2018) Enhancing light harvesting and charge separation of Cu2O photocathodes with spatially separated noble-metal cocatalysts towards highly efficient water splitting. J. Mater. Chem. A 6:20393–20401

    Article  CAS  Google Scholar 

  18. 18.

    Kim JK, Shi X, Jeong MJ, Park J, Han HS, Kim SH, Guo Y, Heinz TF, Fan S, Lee CL, Park JH, Zheng XL (2018) Enhancing Mo:BiVO4 solar water splitting with patterned Au nanospheres by plasmon-induced energy transfer. Adv. Energy Mater 8:1701765–1701769

    Article  CAS  Google Scholar 

  19. 19.

    Ou M, Wan S, Zhong Q, Zhang S, Song Y, Guo L, Cai W, Xu Y (2018) Hierarchical Z-scheme photocatalyst of g-C3N4@Ag/BiVO4 (040) with enhanced visible-light-induced photocatalytic oxidation performance. Appl. Catal. B: Environ 221:97–107

    CAS  Google Scholar 

  20. 20.

    Regmi C, Dhakal D, Lee SW (2018) Visible-light-induced Ag/BiVO4 semiconductor with enhanced photocatalytic and antibacterial performance. Nanotechnology 29:064001–064016

    Article  CAS  Google Scholar 

  21. 21.

    Xu X, Du M, Chen T, Xiong S, Wu T, Zhao D, Fan Z (2016) New insights into Ag-doped BiVO4 microspheres as visible light photocatalysts. RSC. Adv 6:98788–98796

    Article  CAS  Google Scholar 

  22. 22.

    Li M, Xu G, Guan Z, Wang Y, Yu H, Yu Y (2019) Synthesis of Ag/BiVO4/rGO composite with enhanced photocatalytic degradation of triclosan. Sci. Total Environ 664:230–239

    Article  CAS  Google Scholar 

  23. 23.

    Yang C, Li F, Li T (2015) A one-step ionic liquid-assisted ultrasonic method for the preparation of BiOCl/m-BiVO4 heterojunctions with enhanced visible light photocatalytic activity. CrystEngComm 17:676–7683

    Google Scholar 

  24. 24.

    Baral B, Reddy KH, Parida KM (2019) Construction of M-BiVO4/T-BiVO4 isotype heterojunction for enhanced photocatalytic degradation of norfloxacine and oxygen evolution reaction. J. Colloid Interf. Sci 554:278–295

    Article  CAS  Google Scholar 

  25. 25.

    Song M, Wu Y, Xu C, Wang X, Su Y (2019) Synergistic effects of multi-active sites in silver modified Bi°-BiVO4 toward efficient reduction of aromatic nitrobenzene. J. Hazard. Mater 368:530–540

    Article  CAS  Google Scholar 

  26. 26.

    Su Y, Zhu B, Guan K, Gao S, Lv L, Du C, Peng L, Hou L, Wang X (2012) Particle size and structural control of ZnWO4 nanocrystals via Sn2+ doping for tunable optical and visible photocatalytic properties. J Phys. Chem C 116:18508–18517

  27. 27.

    Biesinger MC, Lau LWM, Gerson AT, Smart RSC (2012) The role of the auger parameter in XPS studies of nickel metal, halides and oxides. Phys. Chem. Chem. Phys 14:2434–2442

    Article  CAS  Google Scholar 

  28. 28.

    Xu M, Wang Y, Geng J, Jing D (2017) Photodecomposition of NOx on Ag/TiO2 composite catalysts in a gas phase reactor. Chem. Eng. J 307:181–188

    Article  CAS  Google Scholar 

  29. 29.

    Safaei J, Ullah H, Mohamed NA, Noh MFM, Soh MF, Tahir AA, Ludin NA, Ibrahim MA, Isahak WNRW, Teridi MAM (2018) Enhanced photoelectrochemical performance of Z-scheme g-C3N4/BiVO4 photocatalyst. Appl. Catal. B: Environ 234:296–310

    CAS  Google Scholar 

  30. 30.

    Somsongkul V, Lang F, Jeong AR, Rusu M, Arunchaiya M, Dittrich T (2014) Hole blocking PbI2/CH3NH3PbI3 interface. Phys. Status Solidi-R 8:763–766

    Article  CAS  Google Scholar 

  31. 31.

    Liu X, Liu Y, Gao F, Yang Z, Liu S (2016) Photoinduced surface voltage mapping study for large perovskite single crystals. Appl. Phys. Lett 108:181604–181603

    Article  CAS  Google Scholar 

  32. 32.

    Cheng J, Sprik M (2010) Aligning electronic energy levels at the TiO2/H2O interface. Phys. Rev. B 82:081406–081417

    Article  CAS  Google Scholar 

  33. 33.

    Wu D, Yue S, Wang W, An T, Li G, Yip HY, Zhao H, Wong PK (2016) Boron doped BiOBr nanosheets with enhanced photocatalytic inactivation of Escherichia coli. Appl. Catal. B: Environ 192:35–45

    Article  CAS  Google Scholar 

  34. 34.

    Xia D, Wang W, Yin R, Jiang Z, An T, Li G, Zhao H, Wong PK (2017) Enhanced photocatalytic inactivation of Escherichia coli by a novel Z-scheme g-C3N4/m-Bi2O4 hybrid photocatalyst under visible light: The role of reactive oxygen species. Appl. Catal. B: Environ 214:23–33

    Article  CAS  Google Scholar 

  35. 35.

    Khachatryan L, Vejerano E, Lomnicki S, Dellinger B (2011) Environmentally Persistent Free Radicals (EPFRs). 1. Generation of reactive oxygen species in aqueous solutions. Environ. Technol 45:8559–8566

    Article  CAS  Google Scholar 

  36. 36.

    Wang H, You C, Tan Z (2018) Enhanced photocatalytic oxidation of SO2 on TiO2 surface by Na2CO3 modification. Chem. Eng. J 350:89–99

    Article  CAS  Google Scholar 

  37. 37.

    Tang J, Zou Z, Ye J (2007) Efficient photocatalysis on BaBiO3 driven by visible light. J. Phy. Chem. C 111:12779–12785

    Article  CAS  Google Scholar 

  38. 38.

    Bard AJ, Parsons R, Jordan J (1985) Standard potentials in aqueous solution. Marcel Dekker, New York, pp 70–77

    Google Scholar 

  39. 39.

    Nosaka Y, Nosaka AY (2017) Generation and detection of reactive oxygen species in photocatalysis. Chem. Rev 117:11302–11336

    Article  CAS  Google Scholar 

  40. 40.

    Ishibashi K, Fujishima A, Watanabe T, Hashimoto K (2000) Quantum yields of active oxidative species formed on TiO2 photocatalyst. J. Photoch. Photobio. A 134:139–142

    Article  CAS  Google Scholar 

Download references


Not applicable.


This work is financially supported by the National Natural Science Foundation of China (Grants 21563021 and 21872074), the Inner Mongolia Natural Science Foundation (grant no. 2016JQ01), and Program for Young Talents of Science and Technology in Universities of Inner Mongolia Autonomous Region (NJYT-18-A01).

Author information




YT synthesized and characterized the samples. YS and HG analyzed and discussed the results of the experiments. AD and YS revised the manuscript. All authors read and approved the final manuscript.

Corresponding authors

Correspondence to Alideertu Dong or Yiguo Su.

Ethics declarations

Competing Interests

The authors declare that they have no competing interests.

Additional information

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Supplementary information

Additional file 1: Fig. S1.

XRD patterns of BiVO4 prepared at different pH value. Fig. S2. (a) XRD patterns of pure tz-BiVO4 and tz-BiVO4 samples loaded with various Ag content. (b)XRD patterns of pure ms-BiVO4 and ms-BiVO4 samples loaded with various Ag content. Fig. S3. Elemental composition profiles of Ag/tz-BiVO4. Fig. S4. XPS spectra of ms-BiVO4 and Ag/ms-BiVO4 samples: (a) Bi 4f, (b) V 2p, (c) O 1 s, (d) Ag 3d. Fig. S5. Crystal model of (a) tz-BiVO4, (b) ms-BiVO4. Fig. S6. Crystal model of (a) Ag/tz-BiVO4 (200), (b) Ag/ms-BiVO4 (121). Fig. S7. Band structure of (a) tz-BiVO4, (b) Ag/tz-BiVO4, (c) ms-BiVO4 and (d) Ag/ms-BiVO4. Fig. S8. Transformed Kubelka-Munk function ((αhν)2) versus light energy. Fig. S9. (a) UV-vis diffuse reflectance spectra of tz-BiVO4 and samples loaded with various wt% of Ag. (b) UV-vis diffuse reflectance spectra of ms-BiVO4 and samples loaded with various wt% of Ag. Fig. S10. Photocatalytic inactivation of E.coli and S.aureus by Ag/tz-BiVO4 photocatalysts under VL irradiation. Fig. S11. Photocatalytic inactivation of E.coli by tz-BiVO4 and samples loaded with various wt% of Ag under VL irradiation (a). Photocatalytic inactivation of E. coli by tz-BiVO4 and samples loaded with various wt% of Ag under VL irradiation (b). Fig. S12 Photocatalytic degradation of MB dye solution by tz-BiVO4 and samples loaded with various wt% of Ag under visible light irradiation (a). Photocatalytic degradation of MB dye solution efficiencies with respective scavengers in the presence of Ag/tz-BiVO4 (b). Fig. S13. EPR spectra of •OH in the presence of tz-BiVO4 (a), Ag/tz-BiVO4 (b) ms-BiVO4 (c) and Ag/ms-BiVO4 (d) under dark and VL irradiation. Fig. S14. EPR spectra of DMPO-•O2- in the presence of tz-BiVO4 (a), Ag/tz-BiVO4 (b) ms-BiVO4 (c) and Ag/ms-BiVO4 (d) under dark and VL irradiation. S15. The conducted band edge energy of a semiconductor. Table S1. Lattice parameters of the as-prepared samples. Table S2. Atomic Populations (Mulliken) of BiVO4 and Ag/BiVO4. Table S3. Comparison of Bactericidal Performance of photocatalysts.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Guan, H., Tian, Y., Dong, A. et al. Understanding the Structural-Dependent Photocatalytic Antibacterial Activity: a Case Study of Ag Modified BiVO4. Nanoscale Res Lett 15, 152 (2020).

Download citation


  • Ag/BiVO4
  • Photocatalysis
  • Structural dependent
  • E. coli inactivation
  • DFT calculation