Synthesis of Bimetallic BiPO4/ZnO Nanocomposite: Enhanced Photocatalytic Dye Degradation and Antibacterial Applications

Multidrug-resistant strains (MDRs) are becoming a major concern in a variety of settings, including water treatment and the medical industry. Well-dispersed catalysts such as BiPO4, ZnO nanoparticles (NPs), and different ratios of BiPO4/ZnO nanocomposites (NCs) were synthesized through hydrothermal treatments. The morphological behavior of the prepared catalysts was characterized using XRD, Raman spectra, PL, UV–Vis diffuse reflectance spectroscopy (UV-DRS), SEM, EDX, and Fe-SEM. MDRs were isolated and identified by the 16s rDNA technique as belonging to B. flexus, B. filamentosus, P. stutzeri, and A. baumannii. The antibacterial activity against MDRs and the photocatalytic methylene blue (MB) dye degradation activity of the synthesized NPs and NCs were studied. The results demonstrate that the prepared BiPO4/ZnO-NCs (B1Z4-75:300; NCs-4) caused a maximum growth inhibition of 20 mm against A. baumannii and a minimum growth inhibition of 12 mm against B. filamentosus at 80 μg mL−1 concentrations of the NPs and NCs. Thus, NCs-4 might be a suitable alternative to further explore and develop as an antibacterial agent. The obtained results statistically justified the data (p ≤ 0.05) via one-way analysis of variance (ANOVA). According to the results of the antibacterial and photocatalytic study, we selected the best bimetallic NCs-4 for the photoexcited antibacterial effect of MDRs, including Gram ve+ and Gram ve− strains, via UV light irradiation. The flower-like NCs-4 composites showed more effectiveness than those of BiPO4, ZnO, and other ratios of NCs. The results encourage the development of flower-like NCs-4 to enhance the photocatalytic antibacterial technique for water purification.


Introduction
Over the past several decades, water pollution, usually caused by dye-based industries, has often resulted in the environment posing a potential risk to human health and ecological Int. J. Mol. Sci. 2023, 24,1947 2 of 15 systems [1][2][3]. Water quality is an emerging property of a complex system composed of microbial populations, and wastewater containing harmful dyes poses a major problem to the aquatic environment [4,5]. Approximately 1.84 billion metric tonnes of wastewater from industrial dyes (textiles, paper, food, and pharmaceuticals) are produced every year [6], and 17 million people die worldwide from infectious diseases caused by microbial pathogens [7]. Effluent can be purified via physical, chemical, and biological treatment technologies which are necessary to protect the aquatic environment [8]. The photocatalytic degradation in environmental remediation has attracted increasing interest owing to its eco-friendly merits and decolorization of dye-contaminated wastewater [9].
In addition, the naturally occurring microbial contamination of the aquatic environment by multidrug-resistant (MDR) microbes seriously threatens public health and national priorities around the world [10,11]. The World Health Organization (WHO) has professed that water contaminated by various types of organisms such as bacteria, viruses, and protists has become a great threat to human health [12]. Recently, microbial contamination of water bodies has had a strong impact on animal and human life. Nanotechnology has emerged through the integration of photocatalytic water treatment to develop environmentally friendly technologies for the fabrication of nanomaterials. World scientists and researchers have focused on semiconductor nanoparticles (NPs) or nanocomposites (NCs) as novel catalysts, with considerable interest in their potential applications [13]. They represent promising alternatives to photocatalytic technology that are inexpensive and highly efficient for water purification.

Characterization of As-Prepared NPs and NCs Catalysts
In recent years, nanotechnology has demonstrated considerable potential applications, such as in photocatalysis, photography, optics, electronics, optoelectronics, information storage, luminescence tagging, labeling, administration of medical drugs, and imaging by employing metal particles of the nanoscale size range [25,26]. Semiconductor nano-based photocatalytic technology has gained growing attention due to its highly efficient, lowcost, and eco-friendly removal of organic dye contaminations. Crystalline properties of the as-prepared BiPO 4 -NPs (NPs-1), ZnO-NPs (NPs-2), BiPO 4 /ZnO-NCs (B1Z1-300:300; NCs-1), BiPO 4 /ZnO-NCs (B2Z1-300:150; NCs-2), BiPO 4 /ZnO-NCs (B4Z1-300:75; NCs-3), and BiPO 4 /ZnO-NCs (B1Z4-75:300; NCs-4) were first evaluated by XRD, and the results are demonstrated in Figure 1a. (B1Z1-300:300; NCs-1), BiPO4/ZnO-NCs (B2Z1-300:150; NCs-2), BiPO4/ZnO-NCs (B4Z1-300:75; NCs-3), and BiPO4/ZnO-NCs (B1Z4-75:300; NCs-4) were first evaluated by XRD, and the results are demonstrated in Figure 1a. The XRD results revealed the as-prepared samples' crystalline nature, which agrees with the standard data (JCPDS No. 15-0767) for hexagonal BiPO4 with P21/n space group symmetry. Chengsi et al. [27] reported that upon heating, BiPO4 undergoes a phase shift from hexagonal to monoclinic. The coordination number around Bi 3+ differs between the hexagonal and monoclinic phases of BiPO4. The hexagonal BiPO4 is a new type of inorganic non-metal salt of oxy-acid photocatalyst, Bi 3+ ions that are surrounded by eight nearneighbor oxygen atoms forming square anti-prism geometry around Bi 3+ , whereas in monoclinic BiPO4, Bi 3+ has a coordination number of nine and it exhibits better photocatalytic activity [28]. Furthermore, the crystalline size of the as-prepared pure NPs and NCs was estimated using the Debye Scherer equation [29,30] as follows: where K is the Scherer constant (k = 0.9), λ is the wavelength of the X-ray (λ = 1.5406), β is the full width at half maximum (FWHM), and cos θ is the Bragg angle. Similarly, the diffraction peaks of ZnO are strongly correlated with the hexagonal phase ZnO reported in the JCPDS data (No. . XRD spectra indicate that the sample ZnO nanoparticles consist of a pure phase, with no distinctive peaks for other impurities. The comparison intensities of the peaks at 21.4°, 27.2°, and 31.2° were noticeably elevated in the BiPO4/ZnO nanocomposites when the concentration of BiPO4 increased. This indicates that no other The XRD results revealed the as-prepared samples' crystalline nature, which agrees with the standard data (JCPDS No. 15-0767) for hexagonal BiPO 4 with P2 1 /n space group symmetry. Chengsi et al. [27] reported that upon heating, BiPO 4 undergoes a phase shift from hexagonal to monoclinic. The coordination number around Bi 3+ differs between the hexagonal and monoclinic phases of BiPO 4 . The hexagonal BiPO 4 is a new type of inorganic non-metal salt of oxy-acid photocatalyst, Bi 3+ ions that are surrounded by eight near-neighbor oxygen atoms forming square anti-prism geometry around Bi 3+ , whereas in monoclinic BiPO 4 , Bi 3+ has a coordination number of nine and it exhibits better photocatalytic activity [28]. Furthermore, the crystalline size of the as-prepared pure NPs and NCs was estimated using the Debye Scherer equation [29,30] as follows: where K is the Scherer constant (k = 0.9), λ is the wavelength of the X-ray (λ =  [31]. The Raman spectra for as-synthesized nanocomposites are shown in Figure 1b. The observed intense bands at lower wavenumber regions at 168 cm −1 , 230 cm −1 , and 280 cm −1 can be assigned to the stretching vibration of Bi-O bonds. The two bands centered at higher energies of 1040 cm −1 and 966 cm −1 are attributed to the asymmetric (γ3) and symmetric (γ1) stretching vibrations of the P-O bonds in the PO 4 group, respectively. The bands in the region at 598 cm −1 and 555 cm −1 correspond to the γ4 bending vibration modes of the PO 4 tetrahedron. The weak bands at 460 cm −1 and 404 cm −1 can be ascribed to the γ2 bending modes of the PO 4 units. A sharp, strong, and dominant peak at 438 cm −1 is attributed to the non-polar, high-frequency optical phonon Raman mode (E 2H ), a characteristic peak of the wurtzite hexagonal phase of ZnO. In addition, the peak at 300 cm −1 is assigned to the E 2H -E 2L (multi-phonon scattering) mode and the A1 (longitudinal optical) mode arising at 1160 cm, respectively. A peak that appears at 935 cm −1 corresponds to a second-order multi-phonon scattering mode (2E 2H + E 2L ). Figure 1c shows the UV-Vis diffuse reflectance spectra (UV-DRS) of the as-prepared BiPO 4 -ZnO composite photocatalyst. Strong absorption bands centered at 216 nm and 256 nm have been assigned to the charge transfer (C-T) transition, which originates predominantly from the hybrid electrons of Bi 3+ and O 2− . The light absorbance of pure ZnO is in the UV region, with an absorption edge at 355 nm, and a band-gap around 3.8 eV. Due to the electron transitions from the valence band to the conduction band (O 2p -Zn 3d ), a band at 360 nm might be attributed to the intrinsic band-gap absorption of ZnO. The corresponding band-gap energies (E g ) of composites were calculated using K-M theory and plotted as [F(R) hν] 2 versus photon energy, and it was found to be 3.42 eV, which is shown in the inset of the image. It seems pertinent that the as-synthesized nanocomposite can be excited under UV light exposure, consequently resulting in higher photocatalytic degradation activity.
The PL spectra of the pure BiPO 4 , ZnO, and combined BiPO 4 /ZnO nanocomposites are presented in Figure 1d. The PL excitation spectrum was measured by monitoring the emission wavelength of 325 nm and the visible region of broad peaks from 325 to 600 nm [32]. The Bi 3+ exhibits an emission band centered at 356 nm under UV light excitation due to the transition from 3 P 1 to 1 S 0 of Bi 3+ . A sharp intensity peak observed in the ultraviolet (UV) region around 395 nm corresponds to near-band-edge excitation emission of ZnO. A blue-green emission is present in the range of 470-575 nm. The PL emission peaks at lower energy correspond to zinc vacancies (V zn ) and antisite defects (O zn ). Around 575 nm, green band emissions are ascribed to the existence of a single ionized oxygen vacancy in ZnO. The emission is caused by the radioactive recombination of a photogenerated hole with an electron occupying the oxygen vacancy. It is known that O vacancy is one of the most important factors for narrowing the band-gap of ZnO. Visible luminescence is mainly due to defects related to deep-level emissions, such as Zn interstitials and oxygen vacancies [33].

SEM and Fe-SEM Characterization of NCs-4 Catalysts
The morphological shape and crystallinity size of as-prepared NCs-4 were characterized by SEM and Fe-SEM analysis based on its strong antibacterial activity towards MDRs. The representative SEM images of hexagonal and monoclinic BiPO 4 and ZnO showed nanoparticles with mostly spherical and crystalline and polydispersed-like morphology, as shown in Figure 3a. Fe-SEM images demonstrate that most of the particles are flowershaped, and the particle size distribution chart shows that the prepared nanocomposites have a size range from 30 to 60 nm with an average diameter of about 45 nm, shown in Figure 3b. In the case of BiPO 4 /ZnO, the flower shape was not observed; however, the Fe-SEM image showed the formation of multifaceted clusters of flower morphologies. Because ZnO + has a substantially lower atomic radius than Bi 3+ , doping of BiPO 4 with ZnO resulted in a crystallographic strain of the BiPO 4 lattice. These defect sites in the partially distorted BiPO 4 lattice served as additional nucleation centers. Simultaneous development of numerous nuclei delayed the lattice's pseudo-one-dimensional growth and resulted in multidimensional clusters with reduced overall length. The obtained nanocomposite size distribution for BiPO 4 /ZnO using SEM also agrees well with the sizes provided by Fe-SEM. The EDS elemental mapping results are shown in Figure 3c. The elements Zn, Bi, P, and O present in the nanocomposite spectrum seem to belong to BiPO 4 /ZnO-NCs.

Photocatalytic Experiments
The photocatalytic performances of as-prepared NCs-4 nanocomposites were investigated by degrading methylene blue (MB) dyes under UV light irradiation. Figure 4a shows the photocatalytic degradation activity of the composites under UV light irradiation. Among all samples, BiPO4/ZnO-NCs (B1Z4-75:300; NCs-4) show the highest degradation efficiency under UV light, and almost 96% of the dye (MB) was degraded within 60 min of irradiation, while BiPO4/ZnO-NCs (B1Z4-300:300; NCs-1) reached a constant value after 90 minutes of irradiation and caused 84% degradation. All the pure BiPO4-NPs showed low photocatalytic activity when compared to NPs and NCs. A pseudo-first-order kinetic model was employed to calculate the rate constant [35]. The plot of ln Ct/C0 versus time follows a linear fit, showing that the photocatalytic degradation reaction of MB dye follows pseudo-first-order kinetics, and the corresponding rate constant (k) values were calculated (Figure 4b). After four cycles of the composite, there was no obvious decrease in the photocatalytic MB dye degradation activity, as shown in Figure 4c. Reusing the NCs-4 showed no obvious change in the stability, crystal morphology, or degradability under UV light exposure. The photocatalytic dye degradation activity of NCs-4 was examined with four cycles carried out towards the degradation of MB dye under UV light exposure.

Photocatalytic Experiments
The photocatalytic performances of as-prepared NCs-4 nanocomposites were investigated by degrading methylene blue (MB) dyes under UV light irradiation. Figure 4a shows the photocatalytic degradation activity of the composites under UV light irradiation. Among all samples, BiPO 4 /ZnO-NCs (B1Z4-75:300; NCs-4) show the highest degradation efficiency under UV light, and almost 96% of the dye (MB) was degraded within 60 min of irradiation, while BiPO 4 /ZnO-NCs (B1Z4-300:300; NCs-1) reached a constant value after 90 minutes of irradiation and caused 84% degradation. All the pure BiPO 4 -NPs showed low photocatalytic activity when compared to NPs and NCs. A pseudo-first-order kinetic model was employed to calculate the rate constant [35]. The plot of ln C t /C 0 versus time follows a linear fit, showing that the photocatalytic degradation reaction of MB dye follows pseudo-first-order kinetics, and the corresponding rate constant (k) values were calculated (Figure 4b). After four cycles of the composite, there was no obvious decrease in the photocatalytic MB dye degradation activity, as shown in Figure 4c. Reusing the NCs-4 showed no obvious change in the stability, crystal morphology, or degradability under UV light exposure. The photocatalytic dye degradation activity of NCs-4 was examined with four cycles carried out towards the degradation of MB dye under UV light exposure.  Table 2. The antibacterial interaction of BiPO4/ZnO nanocomposites directly affected the identified osmotic shock of photo-induced holes (H + ) and the hydroxyl radicals ( -OH) that directly attacked MDR cell walls. The nano-flower NCs-4 bimetallic nanocomposites were evidenced as an existent photocatalytic agent that was utilized for MB dye degradation in addition to antibacterial effects [36]. Moreover, in order to assess the activity of the photocatalyst results, they were compared with those of ZnO, TiO2, Fe2O3, BiVO4, nano-heterojunction AgFeO2/ZnO, ZnO-based heterogeneous, Ag/ZnO heterostructural, polyaniline/CdO nanocomposite, Bi2WO6/BiVO4, and Bi2WO6/BiOI p-n heterojunction, which have been widely used for the degradation of organic dyes and controlling microbes [37][38][39][40][41][42][43][44][45][46]. Compared to the standard of AEROXIDE ® TiO2 P-25, our resultant nanopowders are also waterborne and have adequate solubility in water, with a solid white form as well as free-flowing powder with a pH value of 4.5. In addition, similar to AER-OXIDE ® TiO2 P-25, our resultant bimetallic BiPO4/ZnO nanocomposites have a high specific surface area. Due to its unique flower crystalline structure, it is suitable for many catalytic and especially photocatalytic applications. This result clearly shows that the produced nanostructures have equal potential as the standard AEROXIDE ® TiO2 P-25 and can be applicable to photocatalytic degradation, especially on organic pollutants. The results demonstrate that the BiPO4/ZnO-NCs (B1Z4-75:300; NCs-4) catalyst showed significantly superior photocatalytic activity under UV light sources. The photocatalytic degra- The photocatalytic inactivation experiments (MDRs and MB dye) were studied under UV light irradiation with the NCs-4 catalyst. The enumeration study displayed [×10 7 -10 8 CFUs mL −1 ] initial counts of MDR colonies compared to photocatalytically inactivated suspension plates at time intervals of 5 to 20 minutes. The NCs with UV light treatment demonstrated considerable growth inhibition of MDR colonies after 20 minutes, as indicated in Table 2. The antibacterial interaction of BiPO 4 /ZnO nanocomposites directly affected the identified osmotic shock of photo-induced holes (H + ) and the hydroxyl radicals ( -OH) that directly attacked MDR cell walls. The nano-flower NCs-4 bimetallic nanocomposites were evidenced as an existent photocatalytic agent that was utilized for MB dye degradation in addition to antibacterial effects [36]. Moreover, in order to assess the activity of the photocatalyst results, they were compared with those of ZnO, TiO 2 , Fe 2 O 3 , BiVO 4 , nano-heterojunction AgFeO 2 /ZnO, ZnO-based heterogeneous, Ag/ZnO heterostructural, polyaniline/CdO nanocomposite, Bi 2 WO 6 /BiVO 4 , and Bi 2 WO 6 /BiOI p-n heterojunction, which have been widely used for the degradation of organic dyes and controlling microbes [37][38][39][40][41][42][43][44][45][46]. Compared to the standard of AEROXIDE ® TiO2 P-25, our resultant nanopowders are also waterborne and have adequate solubility in water, with a solid white form as well as free-flowing powder with a pH value of 4.5. In addition, similar to AEROXIDE ® TiO 2 P-25, our resultant bimetallic BiPO 4 /ZnO nanocomposites have a high specific surface area. Due to its unique flower crystalline structure, it is suitable for many catalytic and especially photocatalytic applications. This result clearly shows that the produced nanostructures have equal potential as the standard AEROXIDE ® TiO 2 P-25 and can be applicable to photocatalytic degradation, especially on organic pollutants. The results demonstrate that the BiPO 4 /ZnO-NCs (B1Z4-75:300; NCs-4) catalyst showed significantly superior photocatalytic activity under UV light sources. The pho-tocatalytic degradation of organic pollutants is crucial, as it effectively disintegrates the toxicants that pollute environmental waters such as surface and groundwater, causing significant pollution.

Synthesis of BiPO 4 Nanoparticles (NPs)
Precursor solutions of Bi(NO 3 ) 3 .5H 2 O, 4 mmol were dissolved in 60 mL of Milli-Q water along with 5 mL of concentrated HNO 3 under constant stirring until the precursor dissolved. Subsequently, 4 mmol of Na 2 HPO 4 was added drop-wise. Then, the mixed solvent was stirred for 3 h at 70 • C to form a well-homogenized white suspension. Finally, the obtained suspension was transferred to a 100 mL Teflon-lined stainless steel sealer, then autoclaved and maintained at 200 • C for 15 h. After autoclaving, it was allowed to cool for 15 h at room temperature (28 ± 2 • C). After that, the collected solution was centrifuged at 6000 rpm for 30 minutes. Consequently, the supernatant was washed several times with Milli-Q water and dried at 60 • C under vacuum, and the final product containing BiPO 4 was ground into a powder.

Synthesis of BiPO4 Nanoparticles (NPs)
Precursor solutions of Bi(NO3)3.5H2O, 4 mmol were dissolved in 60 mL of Milli-Q water along with 5 mL of concentrated HNO3 under constant stirring until the precursor dissolved. Subsequently, 4 mmol of Na2HPO4 was added drop-wise. Then, the mixed solvent was stirred for 3 h at 70 °C to form a well-homogenized white suspension. Finally, the obtained suspension was transferred to a 100 mL Teflon-lined stainless steel sealer, then autoclaved and maintained at 200 °C for 15 h. After autoclaving, it was allowed to cool for 15 h at room temperature (28 ± 2 °C). After that, the collected solution was centrifuged at 6000 rpm for 30 minutes. Consequently, the supernatant was washed several times with Milli-Q water and dried at 60 °C under vacuum, and the final product containing BiPO4 was ground into a powder.

The Synthesis of Zinc Oxide Nanoparticles (ZnO-NPs)
Wet chemical method ZnO nanoparticles were prepared using a 250 mL round bottom flask (RBF). In a typical process, the aqueous solution of polyethylene glycol (PEG) and 1 M zinc acetate dehydrate [Zn(CH3COO)2.2H2O] were added separately to the flask, and each was dissolved through ultrasound sonication in 30 mL of Milli-Q water for several minutes. Thereafter, 25 mL of the 0.2 M KOH solution was added drop-wise along the walls of the RBF, forming a transparent white solution, and placed on a magnetic stirrer at a constant temperature of 90 °C for 3 h. These solutions were reacted to produce ZnO precipitates that formed a white suspension that was cooled to room temperature. After precipitation, the solution was centrifuged for 30 minutes at 3000 rpm. The supernatant was washed several times using Milli-Q water and dried in a vacuum at 60 °C for 24 h, resulting in the formation of ZnO nano-powder. Finally, it was ground in a mortar

The Synthesis of Zinc Oxide Nanoparticles (ZnO-NPs)
Wet chemical method ZnO nanoparticles were prepared using a 250 mL round bottom flask (RBF). In a typical process, the aqueous solution of polyethylene glycol (PEG) and 1 M zinc acetate dehydrate [Zn(CH 3 COO) 2 .2H 2 O] were added separately to the flask, and each was dissolved through ultrasound sonication in 30 mL of Milli-Q water for several minutes. Thereafter, 25 mL of the 0.2 M KOH solution was added drop-wise along the walls of the RBF, forming a transparent white solution, and placed on a magnetic stirrer at a constant temperature of 90 • C for 3 h. These solutions were reacted to produce ZnO precipitates that formed a white suspension that was cooled to room temperature. After precipitation, the solution was centrifuged for 30 minutes at 3000 rpm. The supernatant was washed several times using Milli-Q water and dried in a vacuum at 60 • C for 24 h, resulting in the formation of ZnO nano-powder. Finally, it was ground in a mortar to powder and stored in the refrigerator at 4 • C until further studies. This experiment was performed eight times at different concentrations under the same process conditions.

Characterization and Property Measurements of As-Prepared NPs and NCs
Crystallite size and phase purity of as-prepared pure nanoparticles and nanocomposites (NPs-1, NPs-2, NCs-1, NCs-2, NCs-3, and NC-4) were analyzed by XRD. The X-ray diffraction (XRD) pattern, recorded by using the Rigaku ULTIMA III with Cu-k α anode radiation (λ = 1.54056 Å), was operated at 40 kV over a 2θ collection range of 20-80 • with a step size of 0.02 • and a scan rate of 4 • per minutes. Raman spectra were recorded for all samples equipped with the laser source at the wavelength (λ) 514.5 nm recorded at room temperature. Photoluminescence (PL) spectra were employed at room temperature with 325 nm as the excitation wavelength, and He-Cd laser as the source of excitation. The optical properties of the composites were analyzed by UV-Vis diffuse reflectance spectroscopy (UV-DRS; JASCO; UV-1700) at a wavelength range of 200-800 nm. The surface morphology, chemical composition, crystallite size, and structure of nanoparticles were characterized by a scanning electron microscope (SEM) (HITACHI; S-3000H) equipped with energy-dispersive spectroscopy (EDS). The size distribution and average size of the nanoparticles were estimated on a field emission scanning electron microscope (Fe-SEM; JSM-6360LA).

Statistical Analysis
The antibacterial susceptibility results are expressed as the mean + SD of the inhibition zone (mm) of three replicates. To understand the relationship between the variables, we used one-way analysis of variance (ANOVA) with ORIGIN8.0 version software; the results were statistically significant if p < 0.05.

Photocatalytic Efficacies of NPs and NCs Catalyst
The photocatalytic dye degradation efficiency was performed under UV light exposure in the presence of NP and NC catalysts (NPs-1, NPs-2, NCs-1, NCs-2, NCs-3, and NC-4). Each NP and NC catalyst was dispersed in 200 mL of a 10 −5 M aqueous MB dye solution. The NP and NC catalysts and multidrug-resistant strain (MDR) suspension were mixed prior to light irradiation. Before UV light irradiation, the suspension (dye and bacterial strains) was magnetically stirred at 150 rpm constantly for 20-30 minutes in dark conditions to obtain an adsorption/desorption equilibrium in the presence of the catalyst. After that, the suspensions were irradiated by UV light (Philips-UV light (150 W); λ = 365 nm). During the test, the degradation efficacy was tested at appropriate time intervals; then, 2 mL of suspension was separated and centrifuged at 10,000 rpm for 30 minutes. The degradation efficiency of MB dye concentrations was monitored through a UV-visible spectroscope (Model-SHIMADZU 1700; 400-800 nm). The dye degradation efficiency percentage (%) was calculated according to the equation by Dai et al. [49]: where C 0 is the initial concentration of MB dye (mg L −1 ), and C is the remaining MB dye concentration (mg L −1 ) of the aqueous solution at a given time under UV light irradiation. Photocatalytic MB dye degradation follows pseudo-first-order kinetics, and the rate constant (k) was estimated by Equation (3): where C t is the concentration of MB after irradiation, C 0 is the concentration of dye before UV light irradiation for reaction time 0 to t (mg L −1 ), and k represents the photocatalytic reaction rate (minutes −1 ).

Photocatalytic Inactivation Experiments
Based on the antibacterial susceptibility test and photocatalytic dye degradation efficiency results, we chose BiPO 4 /ZnO-NCs (B1Z4-75:300; NCs-4) for a photocatalytic inactivation experiment. The photocatalytic inactivation effects on MDR colonies were investigated through an enumeration test, shown in Figure 6. The NCs-4 catalyst was dispersed in 200 mL of 10 −5 M MB dye solution. Then, 100 µL of each MDR (n = 4), including Gram ve + and Gram ve − strains, was blended prior to UV light exposure. Prior to UV light exposure, the MDRs and MB dye suspension were stirred at 150 rpm for 30 minutes in the dark to achieve an adsorption/desorption equilibrium. Then, the suspensions were irradiated using UV light.
After that, the suspensions were irradiated by UV light (Philips-UV light (150 W); λ = 365 nm). During the test, the degradation efficacy was tested at appropriate time intervals; then, 2 mL of suspension was separated and centrifuged at 10,000 rpm for 30 minutes. The degradation efficiency of MB dye concentrations was monitored through a UV-visible spectroscope (Model-SHIMADZU 1700; 400-800 nm). The dye degradation efficiency percentage (%) was calculated according to the equation by Dai et al. [49]: Degradation % = (co −c/co) × 100 (2) where C0 is the initial concentration of MB dye (mg L −1 ), and C is the remaining MB dye concentration (mg L −1 ) of the aqueous solution at a given time under UV light irradiation.
Photocatalytic MB dye degradation follows pseudo-first-order kinetics, and the rate constant (k) was estimated by Equation (3): where Ct is the concentration of MB after irradiation, C0 is the concentration of dye before UV light irradiation for reaction time 0 to t (mg L −1 ), and k represents the photocatalytic reaction rate (minutes −1 ).

Photocatalytic Inactivation Experiments
Based on the antibacterial susceptibility test and photocatalytic dye degradation efficiency results, we chose BiPO4/ZnO-NCs (B1Z4-75:300; NCs-4) for a photocatalytic inactivation experiment. The photocatalytic inactivation effects on MDR colonies were investigated through an enumeration test, shown in Figure 6. The NCs-4 catalyst was dispersed in 200 mL of 10 −5 M MB dye solution. Then, 100 μL of each MDR (n = 4), including Gram ve + and Gram vestrains, was blended prior to UV light exposure. Prior to UV light exposure, the MDRs and MB dye suspension were stirred at 150 rpm for 30 minutes in the dark to achieve an adsorption/desorption equilibrium. Then, the suspensions were irradiated using UV light. For the experiment, 5 mL of the treated (MDRs and MB dye) suspension was collected every 5 minutes and diluted using Milli-Q water. Then, 200 μL of the diluted treated suspension was uniformly spread on nutrient agar (NA) plates, which were incubated at 37 ± 2 °C for 24 h. The control was conducted according to the above procedure without For the experiment, 5 mL of the treated (MDRs and MB dye) suspension was collected every 5 minutes and diluted using Milli-Q water. Then, 200 µL of the diluted treated suspension was uniformly spread on nutrient agar (NA) plates, which were incubated at 37 ± 2 • C for 24 h. The control was conducted according to the above procedure without adding the NCs-4 catalyst. The number of viable colonies was counted with a digital colony counter (make: Medica Gmp; model: 0671m) and is expressed as CFUs mL −1 . Finally, the survival rate was calculated through the following equation: Photocatalytic inactivation (%) = (N Survivor/ N Control ) × 100 (4) where N Control is the MDR colony initial count and N Survivor is the photocatalytic inactivationtreated MDR colony count.

Photocatalytic Cycle Test
The reusability/stability of the NCs-4 catalyst was tested for four cycles under UV light exposure for dye degradation. At the end of the experiment, the NCs-4 catalyst was separated by centrifuging it at 10,000 rpm for 20 minutes and discarding the supernatant solution. Subsequently, the obtained NCs-4 catalyst pellet was rinsed several times with Milli-Q water. Finally, the obtained NCs-4 catalyst pellet was dried at 60 • C for 5 h in a hot air oven; the obtained catalyst powder was further reused for successive degradation. The same procedure was followed for all repeated tests [50].

Conclusions
Based on the above analysis, an efficient hydrothermal method for the synthesis of BiPO 4 /ZnO nanocomposites with different molar ratios was developed. From XRD analysis, the structure of BiPO 4 and ZnO was confirmed. Nanocomposite size was found in the range of 30-60 nm. The charge transfer transition was observed in UV-DRS. The emission and excitation spectra were observed, and the sample showed green emission. The antibacterial activity of flower-like BiPO 4 /ZnO-NCs (B1Z4-75:300; NCs-4) provided a maximum growth inhibition of 18 mm against P. stutzeri and a minimum growth inhibition of 12 mm against B. filamentosus at a concentration of 80 µg mL −1 . The photocatalytic inactivation of MDRs, including Gram ve + and Gram ve − strains, via UV light irradiation using as-prepared NCs-4 exhibited maximal antibacterial activity. The photocatalytic studies on decolorization of MB dye were conducted using all composites (NPs and NCs) that have been established under UV light irradiation. NCs-4 bimetallic nanocomposites exhibited sufficiently enhanced activity. The flower-like NCs-4 bimetallic nanocomposites exhibited the highest degradation of methylene blue (MB) dye of 96% in 60 minutes under UV light irradiation, which supports environmentally safe and cost-effective water treatment.

Conflicts of Interest:
The authors declare that no potential conflict of interest exist. The funding organizations played no role in the study design, data collection and analysis, preparation of the manuscript, or in the decision to publish the results.