Novel Ta/chitosan-doped CuO nanorods for catalytic purification of industrial wastewater and antimicrobial applications.

Novel tantalum (Ta) and chitosan (CS)-doped CuO nanorods (NRs) were synthesized using a single step co-precipitation route. Different concentrations (2 and 4%) of Ta were used in fixed amounts of CS and CuO to examine their catalytic activity and antimicrobial potential. For critical analysis, synthesized NRs were systematically examined using XRD, FTIR HRTEM, EDS, UV-Vis and PL spectroscopy. The XRD technique revealed the monoclinic structure of CuO while an increase in its crystallite size (from 15.5 to 18.5 nm) was observed upon doping. FTIR spectra were examined to study the functional groups of CuO where peaks at 514 cm-1 and 603 cm-1 confirmed the formation of CuO NRs. PL spectra depicted the charge transfer efficiency of the synthesized samples. The presence of dopants (Ta and CS) and constituent elements (Cu, O) was detected using EDS spectra. Additionally, the pH based catalytic performance of fabricated NRs revealed 99.7% dye degradation of toxic methylene blue (MB) dye in neutral media, 99.4% in basic media and 99.5% in acidic media along with promising antibacterial activities for Gram negative/positive bacteria, respectively upon doping of Ta (4%) into CS/CuO. The adsorption energies of CuO co-doped with CS/Ta led to the creation of stable structures that were investigated theoretically using density functional theory. This journal is © The Royal Society of Chemistry.

Introduction

Water pollution has become a serious global concern due to the presence of agricultural pesticides, radiological and industrial discharge, and lack of proper treatment systems. Contaminated water is harmful to human health as well as the environment.[1-3] According to the published statistics, 1–4 million people die annually from water pollution and illnesses.[4] The large volume of waste from organic dyes originating from several industries results in significant environmental pollution.[5] For researchers, removal of toxins from polluted water and the atmosphere has become a major challenge in the last few decades.[6] To deal with this complex issue, many mechanical, physical, and chemical approaches such as adsorption[7,8] ozonation,[7] membrane filtration,[8] coagulation[1] ion exchange[9-11] bio adsorption,[12] photo catalytic degradation,[13,14] biological treatment[15] and catalytic reduction[16] have been used. Transition metal oxides (TMO) are a type of semiconductor that has many applications in magnetic storage devices, electronics, solar energy, photocatalysis and catalysis.[17] Different semiconducting materials such as MnO2, SnO2, CeO2, CaO, ZnO and CuO have been extensively employed as catalysts. Among these semiconductors, CuO is one of the most promising p-type semiconductors due to its superior optical, magnetic and physical properties and is extensively employed in catalysis,[18] solar energy conversion,[19] photocatalysis, gas sensors,[20] as well as field emission.[21] Numerous approaches have been employed to fabricate CuO NRs of diverse shapes and dimensions in recent years including, sonochemical,[22] thermal oxidation,[23] combustion, sol–gel,[24] and co-precipitation methods.[25] Among these methods, co-precipitation has stimulated interest of the industry due to its relatively simple set-up, low energy and undemanding temperature requirements, as well as low cost and efficiency.

Chitosan (CS) has chelating characteristics and interacts with metal oxides including CS/ZnO, CS/TiO2, CS/CdS and CS/Cu2O, to remove dyes, poisonous organics, and antimicrobial agents.[26-32] CuO combined with CS biopolymer can alter the basic metal oxide's biological characteristics. Because of its biocompatibility with biological systems and its nontoxicity, CuO has been widely employed in the food industry and biomedicine as an antioxidant in medication administration and particularly in antibacterial applications.[33] CS has a cationic architecture due to the presence of NH2 and O–H groups, as well as positive charge caused by the presence of strong amino groups.[34,35] It may interact chemically with organic halogen, metal ions, and biomolecules.[36]

Transition metals doped inorganic semiconductors (SnO2, MnO2, ZnO, TiO2 and CuO) exhibit important optical, morphological and magnetic properties.[37] Doping of transition metal tantalum (Ta) (2, 4%) in CuO decreased band gap and enriched optical characteristics of doped specimen and decreased Eg from 3.42 to 3.32 eV.[38] Ta is one of the most appealing materials owing to its broad band gap, high refractive index, large dielectric constant, piezoelectric characteristics, and mechanical stability at high temperatures (2, 3). Furthermore, Ta holds a lot of potential for use in biomedical field such as in coatings for medical applications and surgical tools, as well as for drug delivery, biosensors, and tissue engineering. In this study, co-precipitation approach was utilized to produce Ta/CS-doped CuO NRs for catalytic and antimicrobial applications. The synthesized NRs were used to purify industrial wastewater and remove organic compound namely methylene blue. Doping effect was analyzed by evaluating the optical, structural, and morphological of undoped and doped CuO NRs. The adsorption energies of CS on CuO surface and CS/Ta–CuO surface were calculated using density functional theory calculations.

Experimental section

Materials

Copper chloride (CuCl2·2H2O, 97%), chitosan ((C6H11NO4), 75–85%), sodium hydroxide (NaOH, 98%) and tantalum(v) chloride (TaCl5, 99.8%) were acquired from Sigma-Aldrich (Germany).

Preparation of CuO

CuO nanostructures (NS) were synthesized through co-precipitation technique using copper chloride (CuCl2·2H2O). 0.5 M solution was prepared and heated at 80 °C under constant stirring. Afterward (0.1 M) solution of NaOH was used in the above colloidal solution to maintain pH = 12. Subsequently, colloidal solution was centrifuged for 6 minutes at 7500 rpm, then rinsed 2–3 times with DI water, and dried in oven at 100 °C for 10 hours. Finally, it was powdered to get CuO NRs in the form of black powder.[39]

Synthesis of Ta/CS-doped CuO

0.5 M of CuCl2·H2O was prepared and fixed amount of C6H11NO4 (0.17 g) was added in the above prepared solution with continuous stirring at 80 °C to obtain colloidal solution. Afterward, various concentrations of TaCl5 (2 and 4%) were poured into the solution and heated for 1 hour. Meanwhile, NaOH was used to retain pH = 12 and centrifuged at 7500 rpm for 6 minutes and washed several times with DI water. At the end, precipitates were dried at 100 °C for 10 hours to attain the final product (Fig. 1).

Fig. 1

Schematic diagram of synthesis of Ta/CS–CuO NRs.

Catalytic study

Methylene blue (MB) was used to assess catalytic activity of pristine CuO and (2, 4%) Ta/CS-doped CuO in a solution containing a specific amount of NaBH4 (400 μL, 800 μL) used as a reducing agent in basic, acidic and neutral medium. NRs were added into the solution containing MB and reducing agent, which resulted in substantial degradation. UV-Vis absorption measurements ranging from 200 to 800 nm were used to record the degree of dye degradation.[40,41]

Antibacterial activity

The antimicrobial behavior of produced (2, 4%) Ta/CS-doped CuO NRs was revealed using virulent Staphylococcus aureus (S. aureus) and Escherichia coli (E. coli) bacteria in a well diffusion test. Microbial growth was observed on mannitol sodium acetate (MSA) and MacConkey agar (MCA). On MSA and MCA plates cultured with 0.5 McFarland bacteria growth, wells with an interior diameter of about 6 mm were bored using autoclaved borer.[40,42] Petri dishes were then incubated for 24 hours at 37 °C, and inhibited zones around wells were recorded. The ranges of the inhibition regions around the wells (in mm) reflected the extent of antibacterial activity. Ciprofloxacin (0.005 mg/50 μL) was employed as the standard antibiotic, while DIW (50 μL) was used as the control negative in comparison to different concentrations of synthesized NRs (0.5 and 1.0 mg/50 μL) as least and maximal dosages, accordingly. The plates were inoculated aerobically overnight at 37 °C, and the inhibition areas were determined using a Vernier caliper.[43]

Characterization

Crystalline structure along with phase constitution of materials was characterized with XRD using Bruker XRD, D2 Phase, equipped with (Cu-Kα) radiation. Fourier-transform infrared (FTIR) Perkin Elmer 4000 spectrophotometer was used for chemical analysis and to confirm the presence of related functional groups during synthesis. Absorption spectra in the 200–700 nm wavelength range were measured with UV-Vis spectroscopy (Genesys 10S). Using a spectrofluorometer (JASCO, FP-8300), PL spectra were acquired to investigate the migration and electron–hole pair recombination. HR-TEM (JEOL JEM 2100F) and FESEM JSM-6460LV equipped with an Oxford EDS spectrometer were used to analyze the shape and d-spacing of fabricated specimen.

Results and discussion

To investigate structural properties, crystalline size as well as phase formation of CuO and Ta/CS-doped CuO NRs, XRD was employed in the 2θ range of 10°–80° as depicted in Fig. 2a. The characteristic peaks were noticed at 2θ° = 32.33°, 35.47°, 38.61°, 45,55°, 48.64°, 53.30°, 58.02°, 61.42°, 66.16°, 67.85°, 72.20° and 74.89° corresponding to (110), (−111), (111), (112), (−202), (020), (202), (−113), (−311), (220), (311) and (004) planes of monoclinic CuO, respectively (JCPDS no. 05-0661/01-078-2076).[44] As shown in Fig. 2a, the peak detected around 13.01° confirmed the presence of CS in CuO.[26] Additionally, peaks related to impurities such as TaCl2 and Ta2O5 or other crystalline impurities were not found in tested samples, indicating high-level of purity of prepared specimens. Furthermore, upon addition of CS and Ta in CuO, peaks slightly moved towards the higher diffraction angle. This shift may be due to the size of the Ta5+ ionic radii (0.64 Å) that is less than the ionic radii of CuO (0.73 Å) while Ta5+ ions are more likely to be absorbed into the CuO lattice at low concentrations of Ta5+, making it easier to replace CuO lattice site.[45] The crystallite size of all concerned samples was found to be 15.5, 15.9, 24.8 and 18.6 nm, respectively using Debye–Scherrer's equation.[46]

Fig. 2

(a) XRD pattern and (b) FTIR spectra and (c–e) SAED patterns of pristine and (2, 4%) Ta/CS-doped CuO NRs.

FT-IR was used to examine the functional groups and related vibrational modes in CuO and Ta/CS-doped CuO NRs. Fig. 2b shows high-frequency modes at 514 and 604 cm−1, respectively due to Cu–O stretching vibrations.[44,47] The band found at ∼1350 cm−1 revealed C–N stretching mode of amide group.[48] Peak flexing at ∼1631 cm−1 was attributed to amide group (CONH–), meanwhile, peak at ∼1116 cm−1 verified (O–H) stretching.[49] The band at 3450 cm−1 showed anti-symmetric stretching vibrations of O–H bonds.[50] The absorption peak at ∼2122 cm−1 in CS-doped CuO was mainly attributed to vibration absorption of –CCH group.[51] Peak noticed at ∼2335 cm−1 was designated to stretching vibration of adsorbed CO2.[52] Subsequently, selected area electron diffraction (SAED) images for CuO, CS/CuO and (2, 4%) Ta/CS-doped CuO (Fig. 2c–e) revealed crystalline nature of as-synthesized NRs with indexed spots at (002), (020), (110), (111) and (112) planes that agreed with XRD data thus confirming the monoclinic structure of CuO.

Optical properties of CuO NRs with different doping concentrations were studied using UV-Vis spectroscopy ranging from 200–800 nm (Fig. 3a). The CuO peak with high intensity at ∼362 nm, unveiled the electronic transition from n–π* molecular orbitals of the region.[53,54] However, upon CS doping in CuO, absorbance peak shift toward the lower wavelength (blueshift) was observed, which is mainly due to surface plasmon resonance (SPR).[55] In addition, upon adding of 2, 4% Ta in CS/CuO redshift was noted may be caused by imperfection states, impurities and p–d electrons interaction between metal ions and oxygen produced by Ta dopant as visualized in Fig. 3a.[56,57] The Eg of NRs was extracted from absorption spectra through Tauc plot with corresponding results (Fig. 3b). Calculated Eg of CuO, CS/CuO, (2, 4%) Ta-doped CS/CuO was 3.4, 4.5, 3.32 and 3.29 eV, respectively.[44] The decrement in Eg may be due to defects created in the crystal structure by incorporation of different metal ions.[58]

Fig. 3

(a) Absorption spectra (b) calculated Eg and (c) PL spectra of pristine and (2, 4%) Ta/CS-doped CuO.

Photoluminescence (PL) spectra were acquired to explore optical properties, variation in electron transfer efficiency and recombination rate of excited electrons and holes as shown in Fig. 3c.[59] The visible emission peak at ∼391 nm which is related to violet region corresponded to CuO NRs with adjacent band emission and is well consistent with absorption measurements.[59] In pristine CuO spectrum, slight hump of blue band luminescence at ∼488 nm may be caused by interstitial oxygen and transition oxygen vacancy.[59,60] However, doping of (2, 4%) Ta in CS/CuO NRs demonstrated high recombination rate of (e−–h+) pairs and less efficiency of electron transfer.[42]

High resolution TEM analysis revealed detailed morphological information about as-prepared materials morphology. HR-TEM micrographs of CuO and (2, 4%) Ta/CS-doped CuO are presented in Fig. 4. Figure exhibits nanorods-like morphology of as-synthesized pure sample. Fig. 4b–d revealed agglomeration of CS and Ta-doped samples and also shows self-aggregation of nanorods. From HR-TEM images of CuO, CS/CuO and with 2, 4% Ta-doped CuO NRs (Fig. 4a′–d′), d-spacing was calculated and found to be 0.27, 0.25, 0.23 and 0.24 nm, respectively which corresponded to (110), (−111), (111) and (112) planes of CuO and is well consistent with XRD data (JCPDS no. 05-0661/01-078-2076). Gatan software was used to calculate d-spacing for each specimen (Fig. 4a′–d′).

Fig. 4

(a–d) HR-TEM micrographs of pristine CuO and Ta/Cs-doped CuO, respectively; (a′–d′) interlayer d-spacing of CuO and co-doped NRs, respectively.

Micrographs obtained from scanning electron microscopy (FE-SEM) analysis unveiled the surface morphological features of dopant-free CuO, CS/CuO, and (2 and 4%) Ta/Cs co-doped CuO as manifested in Fig. 5a–d, respectively. FE-SEM results indicate the evolution of nanorods (NRs) of CuO, meanwhile the morphology of (2%, and 4%) Ta/CS co-doped CuO is divulged in Fig. 5b–d. The images of NRs doped with 4% Ta/CS concentration exhibited highly agglomerated NRs as expressed in Fig. 5d.

Fig. 5

(a–d) SEM analysis of dopant-free CuO, CS/CuO and (2 and 4%) Ta/Cs co-doped CuO, respectively.

To ascertain the chemical elements of prepared samples, SEM-EDS was used (Fig. 6a–d).[21] Strong peaks of Cu and O verified the successful formation of CuO, whereas CS and Ta peaks in the doped samples showed that CS and Ta atoms have been effectively doped in the lattice of CuO. The pristine sample has Na peaks that could be due to the NaOH used to control the pH during synthesis. The gold coating on the samples reduces the charging effect, giving rise to Au peaks in the spectra.

Fig. 6

(a) EDS spectra of pristine (b) CS/CuO and (c and d) (2, 4%) Ta/CS-doped CuO.

Antimicrobial activity

In the context of S. aureus and E. coli microorganisms, bactericidal potency was investigated as presented in Table 1, illustrating inhibition areas for CuO, CS/CuO and (2%, 4%) Ta/CS-doped CuO NRs. The results indicated synergistic response due to various concentrations of doped CuO NRs. Substantial inhibition areas were measured against S. aureus and E. coli ranges of 3.15–7.35 nm and 2.50–4.20 nm (high dosage), respectively for doped CuO. Ta/CS-doped CuO with 4 wt% doping concentration showed increased bactericidal effectiveness against S. aureus compared to E. coli. Ciprofloxacin (control +ve) revealed diameters of 4.35 and 5.35 nm towards S. aureus and E. coli, respectively. Upon use of higher concentration of Ta, the results showed a significant increase in zone diameter, indicating improved bactericidal activity. Proposed antimicrobial mechanism is shown in Fig. 7.

Bactericidal response of Ta/CS-doped CuO NRs

Specimen	aInhibition region (mm)		bInhibition region (mm)
	0.5 mg/50 μL	1.0 mg/50 μL	0.5 mg/50 μL	1.0 mg/50 μL
CuO	1.35	2.25	4.25	4.40
CS/CuO	1.95	2.50	2.25	3.15
Ta (2%) : CS : CuO	2.65	3.45	3.35	5.20
Ta (4%) : CS : CuO	3.80	4.20	4.40	7.35
Ciprofloxacin	5.35	5.35	4.35	4.35
DIW	0	0	0	0

Measurement of inhibition region for G −ve.

Inhibition areas (mm) against G +ve.

Fig. 7

Schematic diagram of proposed antimicrobial mechanism.

XPS was utilized to evaluate the surface elemental configuration, surface state, and binding energy changes of Ta/CS-doped CuO NRs Fig. 8a–d. The high-resolution spectra of O 1s, Ta 4f, and Cu 2p are illustrated in Fig. 8a–d. The prominent BE peak at 531.9 eV in Fig. 6a is attributed to surface –OH groups in the O 1s spectrum of Ta.[61] The Fig. 8b demonstrates the O 1s peak fitting spectra of CuO, which precisely reveals the distinct influence of oxygen with binding energies of 530.9 and 532.3 eV, correspondingly, for (C–OH) and (C–O–C).[62] The Ta 4f configuration at 21.5 and 23.4 eV corresponds to Ta 4f7/2 and Ta 4f5/2, respectively, implying sample metallic crests, as illustrated in Fig. 8c.[63] The Cu2+ core level apex fitting spectra has a significant peak at 933.3 eV, which coincides with core level of Cu 2p3/2, as depicted in Fig. 8d, confirming the synthesis of two valence copper oxide NRs. Three higher spectra at 935.8, 941.1, and 943.6 eV are projected to impede satellite heights.[64]

Fig. 8

XPS spectra of doped CuO NRs (a) O 1s spectra of Ta (b) and CuO (c) Ta 4f (d) Cu 2p.

Catalytic activity

The dye degradation (MB) for catalysis of pure and (2, 4%) Ta/CS-doped CuO was studied using UV-Vis spectroscopy (Fig. 9). The bare and co-doped NRs showed the maximum degradation (90, 99.1, 99.6 and 99.7%) in neutral medium (pH = 7), (7, 83.1, 99 and 99.4%) in basic (pH = 12), and (99.2, 98.3, 99.4 and 99.4%) in acidic medium (pH = 4). In all mediums, 4% Ta/CS-doped CuO exhibited the highest catalytic activity (Fig. 9a–c). The crystalline structure, geometry, and surface area of NRs have an impact on the catalytic study of these materials. Generally, maximum catalytic efficiency was observed when the surface area of the catalytic was large, since it provided more active sites. Catalytic efficiency increases in acidic medium due to an increase in the formation of H+ ions obtained to absorb NRs surface. In basic medium, increase in the number of –OH groups leads to the oxidation of reduced products and reduction in catalytic effectiveness.[40,65]

Fig. 9

Catalysis of pristine, CS/CuO, Ta/CS-doped CuO in (a) neutral (b) acidic and (c) basic medium.

The dye degradation phenomenon is well explained in Fig. 10. After the breakdown of NaBH4, BH4− becomes an electron donor, transferring electrons to dye MB via CuO, CS/CuO and (2%, 4%) Ta/CS-doped CuO NRs. During MB dye degradation, the most of crucial part is played by (4%) Ta/CS-doped CuO NRs, which accept the electrons and then transfer these electrons.[60,61] Reduction in redox potential may occur which increase in Fermi potential, and which probably is affected by the size of NRs.[7] The size of NRs plays a key role in determining the nature of interfacial potential-barrier, for small particles barrier is small since surface is larger, and vice versa.[7] In this study, efficiency as well as catalysis speed was assessed and found to increase from reference CuO to CS/CuO, (2%) Ta/CS@CuO and (4%) Ta/CS@CuO samples, respectively. This happens because size reduction or increase has inverse dependence upon Ta concentration i.e., high concentration of Ta decreases particle size or in contrast by lowering concentration increases size and vice versa.[62]

Fig. 10

Schematic diagram of catalysis mechanism.

As catalytic stability is an essential factor for catalyst performance, recycling and stability of executed experiment was measured. For concerned samples, the performed experiment was stayed for almost 3 days after UV light exposure for 80 minutes. It was noted that degradation as well as discoloration were still the same as seen in the initial form. Recycling experiment was investigated with recycling of (4%) Ta/CS co-doped CuO only because this divulged promising result for dye degradation as compared to the rest of the prepared specimens as presented in Fig. 11. This experiment was performed up to 4 cycles; which revealed almost the same result as of the actual experiment.

Fig. 11

The plots for C/Covs. time for the recycling of catalytic activity of (4%) Ta/CS co-doped CuO.

Theoretical calculations

To gain an in-depth understanding of the catalytic activity in Ta/CS doped CuO, we carried out first-principles density functional theory computations within the Perdew, Burke, Ernzerhof (PBE) generalized gradient approximation (GGA)[66] for exchange–correlation energy functional, as implemented in the Quantum Atomistix ToolKit (QuantumATK) code.[67] For simulation, the PseudoDojo-medium norm-conserving pseudopotential[68] and cut-off energy of 105 Ha were employed. A 4 × 3 × 1 k-point mesh constructed by the Monkhorst–Pack grid method was used to sample the Brillouin region. To account for the high correlations, GGA + U calculations were carried out using a Hubbard parameter, U, with an effective value (Ueff = 7 eV) for the appropriate description of the Cu 3d electrons.[69,70] The CuO surface was built from the optimized geometry bulk CuO structure with the lattice constants of a = 4.455 Å, b = 3.821 Å, c = 5.175 Å and β = 92.29°, which agree well with theoretical values and experimental measurements.[44,69-71] Because CuO surface along (111) orientation represents the most stable configuration, it was selected as the model for simulating CS adsorption[69] A slab containing of three layers with (4 × 3) supercell size is used to construct the CuO (111) surface (Fig. 12a). A 15 Å vacuum layer was applied between two adjacent slabs to exclude spurious effects owing to periodic boundary condition. The plot of Fig. 12a shows that the upper layer makes up two types Cu and O atoms containing coordinatively unsaturated and coordinatively saturated atoms. However, the coordinatively unsaturated surface oxygen (O3SUF) atom is connected to one coordinatively unsaturated subsurface cooper (Cu3SUB) atom and two coordinatively saturated surface (Cu4SUF) atoms. Moreover, subsurface O4SUB atom is linked to two Cu4SUF atoms on both sides, one Cu3SUB atom, and one Cu4 atom corresponding to the second layer. Cu3SUB–O3SUF bond length is 1.870 Å, while Cu3SUB–O4SUF bond length is 1.942 Å, both of which are significantly less than the Cu–O bond length of 1.964 Å in bulk structure. Cu4SUF and O4SUB have lengths of 1.987 Å and 1.985 Å, respectively, and Cu4SUF–O3SUF has a distance of 1.952 Å, which is larger than the Cu–O bond length (1.964 Å) in bulk structure.

Fig. 12

The optimized structures (a) CuO (111) surface; (b) CS/Ta doped CuO (111) surface (red: O; blue: Cu; green: Ta; brown: C; light blue N; gray: H).

The interaction strength of CS and CuO surface as well as Ta-doped CuO surface is defined by the magnitude of adsorption energy, which is determined using the equation below:[72,73]where Emolecule+slab, Eslab, and Emolecule represent the overall energies of the surface and adsorbed molecule complex, as well as the energy of a clean surface slab and an isolated molecule, respectively. Surface optimization was also achieved by relaxing the two upper layers and maintaining the bulk state of the bottom layer. According to this concept, a negative adsorption energy value indicates a steady adsorption. After optimization, the adsorption energies of CS on the CuO (111) surface and CS/Ta on the CuO (111) surface are −1.26 eV and −1.79 eV, respectively. Both negative values of adsorption energy show that two complexes are favorable thermodynamically. The bond distance of N–Cu3SUB is 2.321 Å for CS on the CuO (111) surface, whereas the N–Cu3SUB bond length is reduced to 2.237 Å in the CS/Ta–CuO (111) surface (Fig. 12b).

Conclusion

In this study, the co-precipitation approach was used to effectively synthesize pristine and co-doped CuO NRs while the obtained NRs were evaluated for efficient catalytic degradation of MB. Bactericidal performance of synthesized material was also evaluated. The effects of Ta and CS dopants on phase constitution, optical properties, surface morphology and elemental composition of (2, 4%) Ta/CS-doped CuO were studied. XRD analysis revealed that NRs have a monoclinic structure whereas crystallite size increased from 15.5 to 18.6 nm upon addition of co-dopants while the presence of CuO and functional groups was confirmed with EDS and FTIR results, respectively. Decrease in Eg from 3.4 to 3.32 eV was recorded for 4% Ta/CS-doped samples. Chemical composition was calculated with EDS which confirmed the presence of constituent elements Cu, O, Ta, S, Na. In comparison to pristine and CS/CuO, co-doped samples showed the maximum degradation performance against MB dye (i.e., 99.4–99.7%). The creation of stable structures was investigated using a theoretical research based on density functional theory to analyze the adsorption properties of the CS/Ta on CuO surfaces.

Data availability

Data would be made available on demand.

Conflicts of interest

There are no conflicts to declare.