Promising performance of chemically exfoliated Zr-doped MoS2 nanosheets for catalytic and antibacterial applications

Nanostructured materials incorporated with biological reducing agents have shown significant potential for use in bactericidal applications. Such materials have also demonstrated considerable efficacy to counter effects of chemical toxicity. In this study, nanostructured molybdenum disulfide (MoS2) was doped with various concentrations (2.5, 5, 7.5, 10 wt%) of zirconium (Zr) using a hydrothermal route in order to assess its antimicrobial and catalytic potential. Doped and control samples were characterized with various techniques. X-ray diffraction (XRD) analysis confirmed the presence of the hexagonal phase of MoS2 and identification of various functional groups and characteristic peaks (Mo bonding) was carried out using FTIR spectra. Micrographs obtained from FESEM and HR-TEM showed a sheet-like surface morphology, while agglomeration of nanosheets was observed upon doping with nanoparticles. To seek further clarity regarding the layered features of S–Mo–S planes, the defect densities and electronic band structure of pure MoS2 and doped MoS2 samples were investigated through Raman analysis. Optical properties of Zr-doped MoS2 nanosheets were assessed using a UV-vis spectrophotometer and the results indicated a red-shift, i.e., movement of peaks towards longer wavelengths, of the material. Dynamics of migration and recombination of excited electron–hole pairs were investigated using PL spectroscopy, which was also used to confirm the presence of exfoliated nanosheets. In addition, the synthetic dye degradation potential of pure and doped samples was investigated in the presence of a reducing agent (NaBH4). It was noted that doped MoS2 showed superior catalytic activity compared to undoped MoS2. The nanocatalyst synthesized in this study exhibited enhanced antibacterial activity against E. coli and S. aureus at high concentrations (0.5, 1.0 mg/50 μl). The present study suggests a cost-effective and environmentally friendly material that can be used to remove toxins such as synthetic dyes and tannery pollutants from industrial wastewater.


Introduction
Lack of availability of clean potable water is an environmental concern that is shared at a global level. As the world's population continues to grow, an estimated 750 million people lack access to safe and clean drinking water. Around 97.5% of the earth's water reservoir is salty which leaves only 2.5% water that is held in reserve for the sustenance of humankind. 1,2 Untreated wastewater emanating from various industries such as, cosmetics, paper, textile and chemical manufacturing not only serves to pollute and diminish an already limited supply of clean water but also creates a hazard for the environment and living species alike. 3 In view of above, it has become of utmost importance to devise innovative ways to purify polluted water in order to make its availability more widespread especially in developing countries where this issue requires immediate attention. Various techniques have been used for this purpose, for instance, photocatalysis, precipitation, reverse osmosis (RO), and adsorption. Among these techniques, adsorption has received widespread attention owing to its simple operation, low energy consumption, high efficiency and cost-effectiveness. It has been shown especially effective for its use in removing dye pollutants from industrial effluence. 4,5 In this context, adsorption properties of carbon, silica gel (SiO 2 ), polymers and activated alumina adsorbents are frequently studied. Carbon is regarded as an excellent adsorbent for the removal of several pollutants in aqueous solutions. 6 Furthermore, some new carbon materials have been developed including carbon nanotubes (CNTs) 7 and carbon nanobers (CNFs) 8 which show a high degree of adsorption during purication process of water. However, the efficacy of these materials is limited to only certain types of pollutants e.g., organic compounds and metal ions. Therefore, there is a continuous need to produce materials that possess improved capability of adsorption for use in applications developed for the treatment of polluted water.
A possible solution may exist in the form of new generation materials produced at nanoscale. Recently, two dimensional (2D) nanomaterials have attracted considerable attention in the area of catalysis, 9 photocatalysis, optoelectronics, and energyrelated elds (ERF) 10 due to its high chemical stability and large surface area. 11 Among these, MoS 2 is an efficient transition metal dichalcogenide (TMD) that has a layered structure similar to graphene. MoS 2 nanomaterial is composed of three stacked atomic layers i.e. Mo atomic layer sandwiched between two sulfur (S) layers held together through weak van der Waals forces across the layer. 12 MoS 2 layers are characterized by short interlayer distance and strong chemical bond forms with each layer which gives rise to high catalytic activity. In this regard, it is envisaged that due to its potentially strong catalytic and photocatalytic activity, exfoliated MoS 2 nanosheets could prove effective for use in applications developed for environmental remediation 13,14 .
Another endemic problem the modern world is beginning to face is the development of resistance to antibiotic drugs in bacteria. The Infectious Diseases Society of America (IDSA) has stated that the worldwide infection of most dreadful bacterial species called ESKAPE pathogens has developed strong antibiotic resistance 15 . A number of deaths have been recorded worldwide caused by these pathogens. Every year, Escherichia coli (E. coli) a family member of ESKAPE pathogen causes death of 1.3 million children under the age of ve due to diarrhea, which is mainly transmitted from contaminated water. To mitigate this enormous loss, a continuous effort is required to develop new antibiotics that could control the bacterial growth of ESKAPE pathogens. In this respect, 2D materials are potential candidates due to their superior antibacterial activity, e.g., graphene oxide (GO) and chemically exfoliated MoS 2 have been shown to work efficiently against several microorganisms 16 . As MoS 2 has a large surface area, it generates strong surface charge mobility and conductivity which might facilitate bacteria adhesion 17 . These materials may be duly effective for use in biomedical applications that do not release any toxic biocide into the environment 18 . MoS 2 has generated great interest due to its antimicrobial activity against pathogens Gram-positive (S. aureus) and Gram-negative (E. coli) 19 . MoS 2 nanocomposites have exhibited rapid and effective reaction for killing bacteria in vitro and wound disinfection in vivo 20 .
Various nanocatalysts such as, Bi, Co, and Cu have been employed so far in an effort to enhance the efficiency of catalytic activity. These catalysts are capable of degrading MB in 3-4 minutes, which is a notable accomplishment 21,22 . In this study, Zr nanoparticles were used as a catalyst to enhance the catalytic and antimicrobial efficiency of MoS 2 prepared through hydrothermal technique. The study revealed that Zr-doped MoS 2 nanosheets were signicantly more effective in removing organic dye (methylene blue) compared to other transitions metals. For this reason, the synthesize product can be considered as a superior candidate for use in antimicrobial applications developed in the near future.

Chemicals
Molybdenum disulde (MoS 2 , 99.8%) and sodium borohydride (NaBH 4 ) were procured from Sigma-Aldrich (Germany) and hydrogen chloride (HCl, diluted 37%) was acquired from Analar chemical lab. Sodium nitrate (NaNO 3 ) and zirconium nitrate hydrate (Zr(NO 3 ) 4 $H 2 O) were received from BDH Laboratories (United Kingdom). Bacterial growth media were of analytical grade provided by TM Media, (Titan Biotech Ltd, India). All chemicals were used in this work without additional purication.

MoS 2 exfoliation process
MoS 2 nanosheets were synthesized via chemical exfoliation route as depicted in Fig. 1. Sodium nitrate (6 g) was dissolved in 16 ml of 37% diluted HCl in single-neck round ask. Later, bulk MoS 2 (1.2 g) was added to the above-mentioned solution, and the reaction was quenched with water. Prepared solution was sonicated at 30 C for 5 hours with toxic gas collection setup. Obtained supernatant fraction was centrifuged at 6000 rpm for 30 minutes. Finally, grey black precipitated MoS 2 nanosheets were collected. 2

Synthesis of Zr-doped MoS 2 nanosheets
Hydrothermal synthesis was used to prepare the desired concentrations of Zr-doped MoS 2 nanosheets as shown in Fig. 1

Materials characterization
Structural and phase information of doped sample was obtained with the help of X-ray diffraction (XRD). PANalytical X'pert equipped with Cu-Ka radiation (l $ 0.154nm) was used by varying diffracted angle 2q from 10 to 65 for this purpose. The presence of various functional groups was identied with FTIR PerklinElmer spectrometer, and optical properties were examined using UV-vis Spectrophotometer (Genesys 10S) set in the range of 250-350 nm. Surface morphology and interlayer spacing was investigated using FESEM, JSM-6460LV and HRTEM Philips CM-30 and JEOL JEM 2100F. To conrm the presence of MoS 2 akes, Raman spectra were recorded on Renishaw with Reex confocal Raman microscope operated at a wavelength of 532 nm (6 mW) laser. Photoluminescence spectra of as-prepared and doped samples were recorded using spectrouorometer (JASCO, FP-8300).

Catalytic potential
The catalytic activity of the undoped and doped MoS 2 nanosheets was assessed in terms of degradation of methylene blue (MB) which acts as an oxidizing agent in the presence of a reducing agent NaBH 4 . In this study, the synthesized product acts as a catalyst. The amount of catalyst used in the reaction is a crucial factor during the regulation of catalytic activity. With increasing concentration of the catalyst, the degree of dye degradation is enhanced since a catalyst minimizes the activation energy required for the reaction to take place. With regards to the experiment method used in the present study, freshly prepared 400 ml solution of sodium borohydride (NaBH 4 ) (0.1 M) was added in 3 ml aqueous methylene blue (10 ppm) in a quartz cell. This was followed by the addition of 400 ml of Zrdoped nanosheets with specic concentrations (0 : 1, 0.025 : 1, 0.050 : 1, 0.075 : 1, 0.10 : 1) to the solution. Decolorization and variations in absorption intensity of the dye represented the reaction rate over periodic intervals as shown in Fig. 2. Reaction without nanocatalyst is referred to as the one with reference sample. UV-vis spectrophotometer was employed to acquire absorption spectra at various intervals in the range of 200-750 nm (Fig. 8).

Isolation and identication of S. aureus and E. coli
Caprine mastitic milk samples collected from various farms of Punjab, Pakistan were cultured on 5% sheep blood agar. The cultured samples were incubated for 24 hours at 37 C and the characteristic colonies thus obtained were further streaked on manitol salt agar (MSA) and MacConkey agar (MA) in order to isolate puried Staphylococcus aureus (S. aureus) and Escherichia coli (E. coli), respectively in triplets. Identication of puried colonies proceeded through Gram's staining, morphological study, and biochemical tests (i.e., catalase and coagulase tests). This journal is © The Royal Society of Chemistry 2020 RSC Adv., 2020, 10, 20559-20571 | 20561

Antibacterial activity
Antibacterial evaluation of Zr-doped MoS 2 nanosheets was conducted using Gram-positive (G +ve) S. aureus and Gramnegative (G Àve) bacteria E. coli directly isolated from caprine mastitis. In vitro antibacterial efficacy was assessed through agar well diffusion test by swabbing S. aureus and E. coli isolates on MSA and MA, respectively. Bacterial suspensions of 1.5 Â 10 8 CFU ml À1 (0.5 Mc-Farland standards) were swabbed on Petri dishes and wells containing 6 mm diameter were formed using a sterile cork borer. Various concentrations of Zr-doped MoS 2 (0.5 mg/50 ml) and (1.0 mg/50 ml) were loaded into each well and compared with ciprooxacin (0.005 mg/50 ml) and DIW (50 ml) as positive and negative control, respectively under aseptic conditions. The loaded Petri dishes were incubated at 37 C for 24 hours and antibacterial evaluation of Zr-doped MoS 2 was conducted with Vernier caliper that measured inhibition zones in millimeter (mm). 2.7.1. Statistical analysis. The antibacterial efficacy, calculated in terms of inhibition zone diameters (mm), was statistically analyzed by one-way analysis of variance (ANOVA) using SPSS 20.

Results and discussion
Crystallinity and phase purity of Zr-doped MoS 2 nanosheets were examined using XRD technique (Fig. 3a) (004), (100), (101), (103), (006), (105) and (106) planes respectively. 2,24,25 Observed reections reveal hexagonal phase without impurity peak, which correlated well with JCPDS card no. 00-37-1492. 20 Low-intensity diffraction peaks indicate low crystallinity of Zr-MoS 2 while the presence of (004) face possibly resulted from partial restacking that occurred when the samples were dried during synthesis. 26,27 Fig. 2 Schematic diagram of the experimental procedure adopted to measure catalytic activity. Peaks observed at (100), (103) and (105) are distinctive MoS 2 peaks, representing crystal planes that are well crystalized and belong to the hexagonal phase of MoS 2 . 28,29 Interlayer spacing of nanosheets at 32.7 (100) was evaluated with Bragg's equation 2d sin q ¼ nl, and was found to be 0.27 nm, which also corroborates the information obtained from HR-TEM images discussed later in Fig. 6. 30 SAED analysis of un-doped and doped MoS 2 was undertaken in a small region inside sphere while a large area exhibits the whole sphere as shown in Fig. 3b-d. Diffraction rings within SAED pattern were indexed as (004), (006) and (100) crystal planes belonging to MoS 2 hexagonal phase, which agreed well with the XRD results.
UV-vis spectroscopy was applied to investigate the optical properties of synthesized Zr-doped MoS 2 nanosheets, as shown in Fig. 4a. MoS 2 nanosheets exhibit broad light absorption in the visible range owing to its intrinsic narrow band gap coupled with multilayer nanostructure. The pristine sample shows a light UV response with an absorbance band at around 225 nm. In case of Zr-doped nanosheets, absorption range is increased with a slight redshi (toward longer wavelength) in UV zone. Redshi is caused by the presence of Zr nanoparticles, which indicates a possible charge-transfer transition between Zr and MoS 2 . 31 FTIR spectra were acquired to identify various functional groups present in the control and doped sample in the range of 4000-400 cm À1 as illustrated in Fig. 4b. Broad and sharp peaks observed at 3454 and 1637 cm À1 belong to symmetrical -OH stretching-vibration and water bending modes. 32 The transmittance band appearing around 2170 cm À1 in the doped sample is attributed to N]C. 33 Peak observed in control sample at $2358 cm À1 represent carbon double bond (CO 2 ), while band at 1124 cm À1 is assigned to S]O bonding vibrations. 33,34 Moreover, peak occurring at $903 cm À1 is related to Mo-O vibration which is in agreement with the formation of MoS 2 that possesses partially-oxidized edges. 35 The morphology and structure of pure and doped MoS 2 was examined using FESEM and the results are shown in Fig. 5a-d. From the images, it can be seen that pure MoS 2 showed nanosheets of plane-surface morphology with a thickness and lateral length of $100 nm (Fig. 5a). Upon doping with Zr-NPs, nanosheets depict the same morphology and lateral length, however the sheet-surface exhibits a rougher appearance (see Fig. 5c). It can also be observed that many nanoparticles are anchored on the surface of nanosheets (Fig. 5b-d). Morphology and microstructure of pure and doped MoS 2 were further characterized with HR-TEM as illustrated in Fig. 5(a 0 -d 0 ). HR-TEM results verify that MoS 2 samples possess layered sheet-like morphology and are somewhat agglomerated. On the other hand, Zr-doped samples present a layered structure with delaminated sheets and dark spots provide evidence for the presence of Zr on MoS 2 nanosheets. 36,37 Detailed characterization of nanosheets were further undertaken with HR-TEM up to 10 nm as depicted in Fig. 6, where surface morphology was observed to exhibit a layered structure in the synthesized products. Integral lattice of sheetlike MoS 2 exhibited no defects or deformation in the samples prepared through exfoliation route. 38 HR-TEM results display ltered micrograph and Fast Fourier Transform [FFT] of the selected area specied by yellow-square in Fig. 6a-d, which provides structural information at a higher resolution. For pure sample, interlayer spacing was calculated as 0.27 nm, which is consistent with the reported data and XRD results. 30,39 Upon doping with Zr-NPs, d-spacing of 0.29, 0.27 and 0.28 nm were measured.
Raman spectroscopy was employed to probe structural properties with regards to the number of layers, defects densities, and electronic band structure. Raman scattering was performed in the range of 100-900 cm À1 (see Fig. 7a). 40 In the observed spectra of the prepared products, peaks are located at 146, 179, 220, 285, 336, 383, 408, 645 and 820 cm À1 , which is consistent with previously reported literature. 41-43 Two This journal is © The Royal Society of Chemistry 2020 RSC Adv., 2020, 10, 20559-20571 | 20563 characteristics peaks were exhibited by all samples, e.g., rstorder active modes that exist in most of the reported Raman studies of MoS 2 . These peaks were assigned as E 2g (383 cm À1 ) indicating in-plane vibrational mode and A 1g (408 cm À1 ) that signify out-of-plane vibrations, these modes are attributed to the layered structure of S-Mo-S planes. 41 Due to the dependence of these two modes on the number of layers of MoS 2 , sharpness of peaks is slightly decrease with an increase in the inserted species may be attributed to laser-induced heating phenomenon. 40,43 Peaks around 145 and 179 cm À1 are assigned to E 2g -LA(M) and A 1g (M) -LA(M) phonon mode, respectively. 41,44 The 645 cm À1 band is a combination of LA(M) frequency and A 1g mode, while the 176 cm À1 band arises due to subtraction of LA(M) from A 1g frequency (408 cm À1 ), as shown in Fig. 7b. 41 Energy of LA(M) phonon determined from the procedure is somewhat larger than the value determined from the energy of 2LA(M) peak in non-resonant spectrum. 45 The peak observed at 820 cm À1 is attributed to the second secondorder spectral region (2A 1g ). 32 Photoluminescence (PL) was employed to elucidate the electron-hole pair recombination process of the control and Zrdoped sample, as shown in Fig. 7c. It is an effective way to characterize 2D MoS 2 as its PL effect is strongly associated with its electronic-band structure. 46 Bulk MoS 2 has 1.2 eV of indirect band gap whereas exfoliated MoS 2 , which makes a transition from indirect band gap to direct band gap of 1.8 eV, has enhanced PL owing to relaxation-of-excitons at Brillouin zone K point. 47 It is observed in 2D MoS 2 nanosheets that an increase in excitation wavelength proceeds to a redshi in PL spectrum with l-range from 480 to 540 nm. This observation is associated to the excitation dependent PL is related with poly-dispersity of two-dimensional nanosheets. 48 Observed peak around 543 nm   is attributed to E 2g vibrational mode associated with in-plane vibrations of S atoms, as also discussed in Raman spectra. 49 Upon doping with Zr, two absorptions band appeared at $557 and 613; peak at 557 nm can be attributed to nanosheets with lateral dimensions of a few tens of nm. 50 The peaks located at 613 nm signify-B direct excitonic-peak. 51 The above-stated results acquired from the analysis of MoS 2 nanosheets suggest quantum connement effect.
XPS analysis shows the composition of Zr-doped MoS 2 nanosheets with the presence of O, C, Zr, and Mo as illustrated in Fig. 8a-d. The Mo 3d spectra were recorded and deconvoluted as presented in Fig. 8a-d. All observed peaks of O, C, Zr and Mo accord with existing reports. [56][57][58] The two peaks present in the spectra of O1s region conrmed the existence of two types of oxygen species on the surface, see Fig. 8a. The peak positioned at 531.3 eV in Fig. 8a could be assigned to silanol group for O1s species. 59 The two peaks seen at 162.7 and 160.8 eV correspond to the presence of polysulde in MoS 2 as depicted in Fig. 8b. Zr 3d 3/2 and Zr 3d 5/2 were observed at 182.5 eV and 184.7 eV, respectively, see Fig. 8c. In catalyst, Zr binding energy is greater than pure Zr metal (180.0 eV). It is lower than 182.9 eV in ZrO 2 and similar with ZrOx at 181.4 eV. 60 Conclusively, it is clear that Zr cations were effectively incorporated within MoS 2 . 59 In Fig. 8d, Mo 3d spectra veried various oxidation states of Mo atoms as Mo 4+ , Mo 5+ and Mo 6+ . 61 Mo 3d 5/2 and Mo 3d 3/2 binding energies indicate different oxidative states of Mo ions in the synthesized material. 62 To assess the potential of Zr-doped MoS 2 nanosheets, MB was used as contaminant to determine the catalytic activity in environmental remediation process. Catalytic degradation of organic dye (MB) was investigated using sodium borohydride (NaBH 4 ) as a reducing agent while Zr-doped MoS 2 was employed as a nanocatalyst. The reaction was examined in the range of wavelength 500-750 nm using UV-vis spectrometer. In an aqueous medium, the absorption peak of MB was observed at 665 nm. Reducing ability of NaBH 4 with MB and MoS 2 was not observed to be signicant, as it degraded 5% and 36% of MB only in 40 min respectively, as presented in Fig. 9a. Concentration of methylene blue continuously decreased within an increase in doping concentration of Zr in MoS 2 and the maximum catalytic efficacy was noted for 0.1 : 1 (see Fig. 9f). In the presence of a catalyst, reduction of the dye was accelerated, which is represented by a sharp decrease in the absorption peak of MB. Catalysts facilitate electron relay from donor (BH 4 ) to acceptor (MB), in which case catalysts accept electrons from BH 4 ions and transfer them to MB.
It was observed that the sample doped with a lower concentration of dopant (0.025 : 1 sample) showed incomplete reduction of dye with 40% degradation of MB in 21 min (Fig. 9c). The (0.05 : 1) and (0.075 : 1) samples reduce methylene blue within 13 and 1.5 min and degrade MB 68% and 89% respectively, and 0.1 : 1 sample accomplishes almost complete reduction (about 99%) of methylene blue to leuco-methylene blue (LMB) in 1 min at 25 C. The successive decrease in absorption intensity of dye demonstrated a rapid reaction rate over a certain period. 52 Besides, signicant catalytic efficiency was observed for 0.1 : 1 sample (see Fig. 9g and h), suggesting that Zr-doped MoS 2 is an excellent and efficient nanocatalyst for use in degradation of organic dyes.
According to Beer Lambert's law, the ratio of the concentrated amount of MB at any time (C t ) and initial concentrated amount (C o ), namely C t /C o can be evaluated using different concentrations of absorbance (A t /A o ). Fig. 9g and 10 elucidate C t /C o time course for prepared catalysts, which further indicates the catalytic reaction for catalysts used. Furthermore, reduction of MB was almost complete at the end of reaction period, indicating the important role played by Zr-doped MoS 2 . The dye degradation potential (measured in percentages) of all synthesized samples are shown in Fig. 9h, which was calculated using eqn (1): The pH value is an important factor in wastewater management. pH playes a vital role in the dye degradation reaction. In the present work, pH value was observed to be basic (7.9).
Stability also greatly inuences the performance of catalysts during dye degradation reaction. To check the stability of catalysts, both activities were retained for 48 hours, aer which duration the same results were observed as before. As degradation remained undisturbed, it indicated high stability of the catalysts. In the present work, reusability or recyclability of catalyst was assessed by recycling 7.5 and 10 wt% of Zr-doped MoS 2 . These particular catalyst samples were selected since they outperformed others in earlier experiments. The selected samples were examined for three cycles as can be seen in Fig. 10a and b. Furthermore, the load of catalyst was also veri-ed before and aer three recycling procedures. In Fig. 10a and b small weight loss of catalyst was detected i.e., ranging from 2 mg (before) to 1.6 mg (aer three cycles) as determined by deliberating $5% sensing deviation. From the above ndings, Zr-doped MoS 2 catalysts are considered to be highly stable during catalytic reactions showing remarkable catalytic potential for use in the treatment of industrial wastewater.
The in vitro antibacterial efficacy of Zr-doped MoS 2 nanosheets through agar well diffusion method against E. coli and S. aureus are shown in Fig. 11a-h Fig. 11a-h while, 2.5 and 5 wt% doping showed null activity against both bacteria at low concentrations as can be seen in comparative analysis exhibited in Fig. 11i. Oxidative stress of fabricated nanostructures depends upon the size and concentration of nanoparticles. It is know that the size of nanoparticles inuences anti-bacterial efficacy. 53,54 Small-sized particles generate reactive oxygen species (ROS) which enclose bacterial cell membrane through extrusion of cytoplasmic contents, resulting in bacterial death. Other possibilities for the reaction of nanomaterials with bacterial strains include strong interaction of cations with negatively charged parts of bacterial cells resulting in its collapse. 55,63,64

Conclusion
The Zr-doped MoS 2 nanosheets were successfully synthesized through hydrothermal route. Doping of nanosheets was performed with an aim to increase its antimicrobial and catalytic efficiency. The formation of hexagonal phase of MoS 2 was conrmed through XRD analysis. Hexagonal MoS 2 possessed an interlayer spacing of $0.27 nm, which matched well with the results obtained from HR-TEM. FTIR spectra indicated molecular bonding of Mo and S with functional groups, while characteristic transmittance of MoS 2 was observed at $903 and 1124 cm À1 . The surface morphology with an agglomeration of stacking layers was conrmed with FESEM and further evidence about interlayer spacing was attained through HR-TEM with ring feature of prepared specimens. Molecular ngerprint with vibrational modes of E 2g and A 1g conrmed the presence of inplane vibrations of S atoms with respect to Mo atoms and S atomic vibrations in opposite direction to Mo atoms, respectively. It was suggested that the role of Zr in facilitating electron migration and recombination of charge was diminished and efficiency of electron mobility was increased in doped samples. UV-vis spectroscopy was performed and an absorption band in the range of 225 nm with redshi was observed. The present research conrmed that higher concentrations (0.1 : 1) of Zrdoped MoS 2 nanosheets show excellent antibacterial efficacy and unique catalytic response such that it degrades 99% MB in just 1 min. Based on the present study, MoS 2 nanosheets synthesized with specic Zr dopant concentrations have proved to be a novel material with outstanding antimicrobial and catalytic efficacy for use in the area of water purication and biomedical applications.

Availability of data and materials
All data are fully available without restriction.

Conflicts of interest
The authors declare that they have no competing interests.