Composition and method for treating dye wastewater

Abstract

A composition for treating dye wastewater and method of synthesizing said composition, is disclosed. The composition is a catalyst composition used for ultrasound irradiation process. The composition comprises a copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material, and hydrogen peroxide (H.sub.2O.sub.2). Further, the present invention also discloses a method for treating dye wastewater using said nanocomposite catalyst composition. The composition according to the present invention, provides a novel, eco-friendly and economical method for the complete degradation of the organic dye pollutants from the industrial wastewater. Further, the sonocatalyst has enough stability, as its structure and degradation ability does not change even after multiple use. Further, the sonocatalyst could be easily separated and reused from a waste water, without any need for complex separation process.

Claims

1. A method of synthesizing a composition for treating dye wastewater, comprising the step of: a) preparing copper sulfide (Cu.sub.2S) nanoparticle by heating Cu(II) diethyldithiocarbamate complex at predetermined time and temperature; b) adding Cu.sub.2S nanoparticle in deionized water and sonicating them together for preset time to form a suspension; c) adding predetermined quantity of Fe(NO.sub.3).sub.3. 9H.sub.2O and Co(NO.sub.3).sub.2. 6H.sub.2O to said suspension and agitate for preset time; d) adding NaOH solution and stir with resultant solution of step (c) to obtain pH 11; e) heating the resultant solution of step (d) for predetermined time and temperature, and f) cooling the output nanoparticles of step (e) to room temperature, washing and filtering to obtain the sonocatalyst copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material.

2. The method of claim 1, wherein the predetermined temperature for preparing copper sulfide (Cu.sub.2S) nanoparticle at step (a) is 220 C.

3. The method of claim 1, wherein the predetermined time for preparing copper sulfide (Cu.sub.2S) nanoparticle at step (a) is 0.5 h.

4. The method of claim 1, wherein the Cu.sub.2S nanoparticle is sonicated in deionized water at step (b) for 1 h.

5. The method of claim 1, wherein the predetermined quantity of Fe(NO.sub.3).sub.3. 9H.sub.2O and Co(NO.sub.3).sub.2. 6H.sub.2O is agitated with said suspension at step (c) for 1 h.

6. The method of claim 1, wherein the resultant solution of step (d) is heated in autoclave at 180 C. for 12 h.

Description

BRIEF DESCRIPTION OF DRAWINGS

(1) FIG. 1 exemplarily illustrates a method of synthesizing sonocatalyst copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite, according to an embodiment of the present invention;

(2) FIG. 2 exemplarily illustrates a method of treating dye wastewater using said sonocatalyst (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite, according to an embodiment of the present invention;

(3) FIG. 3 exemplarily illustrates a laboratory synthesis process of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite for degrading high concentration of dye pollutants;

(4) FIG. 4 exemplarily illustrates XRD pattern of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite;

(5) FIG. 5 exemplarily illustrates FT-IR spectra of (a) Cu.sub.2S, (b) CoFe.sub.2O.sub.4, and (c) Cu.sub.2S/CoFe.sub.2O.sub.4;

(6) FIG. 6A exemplarily illustrates SEM images of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite at 500 nm;

(7) FIG. 6B exemplarily illustrates SEM images of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite at 1 m;

(8) FIG. 7A exemplarily illustrates EDX analysis of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite;

(9) FIG. 7B exemplarily illustrates EDX mapping elemental image of the Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite;

(10) FIG. 8A exemplarily illustrates room-temperature magnetization curves of CoFe.sub.2O.sub.4;

(11) FIG. 8B exemplarily illustrates room-temperature magnetization curves of Cu.sub.2S/CoFe.sub.2O.sub.4;

(12) FIG. 9 exemplarily illustrates UV-Visible absorbance spectrum of the Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite;

(13) FIG. 10 exemplarily illustrates UV-visible spectral changes of methylene blue (MB) aqueous solution over Cu.sub.2S/CoFe.sub.2O.sub.4, hydrogen peroxide (H.sub.2O.sub.2), and ultrasound irradiation;

(14) FIG. 11 exemplarily illustrates influence of H.sub.2O.sub.2 concentration on the sonocatalytic degradation of MB;

(15) FIG. 12 exemplarily illustrates comparison of change in concentration of MB, rhodamine B (RB) and methyl orange (MO) (C/C.sub.0) as a function of irradiation time for the sonocatalyst;

(16) FIG. 13 exemplarily illustrates schematic of separating generated electrons and holes on the interface of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite under ultrasonic irradiation, and

(17) FIG. 14 exemplarily illustrates recyclability of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite.

DETAILED DESCRIPTION

(18) Amongst the numerous techniques of dye removal treatment, ultrasonic oxidation process gives the best results as it can be used to remove different types of coloring materials. However, the application of ultrasound alone is inefficient for the degradation of the target organic pollutants, because this process requires more time and high amount of energy for an acceptable degradation of dyes.

(19) Therefore, there exists a need for a novel nanocomposite composition for an efficient ultrasonic oxidation process for treating dye effluents or pollutants. There is also need for a composition that consumes less time, energy and allows easy retrieval of the catalyst from reaction mixture for subsequent uses.

(20) The present invention generally relates to a composition for treating or degrading organic dye pollutants from industrial wastewater in short duration. Further, the present invention also relates to a method of synthesizing said composition for treating dye wastewater.

(21) A description of embodiments of the present invention will now be given with reference to the figures. It is expected that the present invention may be embodied in other specific forms without departing from its spirit or essential characteristics. The described embodiments are to be considered in all respects only as illustrative and not restrictive. The scope of the invention is, therefore, indicated by the appended claims rather than by the foregoing description. All changes that come within the meaning and range of equivalency of the claims are to be embraced within their scope.

(22) The present invention discloses a composition for treating dye wastewater, is disclosed. In one embodiment, the composition is a catalyst composition used for ultrasound irradiation process. The composition according to the present invention, comprises a copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material. In one embodiment, the composition further comprises hydrogen peroxide (H.sub.2O.sub.2). In one embodiment, the coercive force (H.sub.c) of the nanocomposite material is 480 Oe. The saturation magnetization (M.sub.s) of the nanocomposite material is 36.26 emu/g. Further, the remnant magnetization (M.sub.r) of the nanocomposite material is 9.85 emu/g. In one embodiment, the nanocomposite material is a sonocatalyst. In one embodiment, the concentration of hydrogen peroxide (H.sub.2O.sub.2) ranges from 0 mM to 5 mM. In some embodiments, the optimum concentration of hydrogen peroxide (H.sub.2O.sub.2) is 4 mM.

(23) Referring to FIG. 1, a method 100 of synthesizing a composition for treating dye wastewater, is disclosed. Said composition is synthesized by a simple hydrothermal method. The method 100 comprises the step of, preparing copper sulfide (Cu.sub.2S) nanoparticle by heating Cu(II) diethyldithiocarbamate complex at predetermined time and temperature at step 102. At step 104, Cu.sub.2S nanoparticle is added in deionized water and sonicating them together for preset time to form a suspension. The method further includes, at step 106, a predetermined quantity of Fe(NO.sub.3).sub.3. 9H.sub.2O and Co(NO.sub.3).sub.2. 6H.sub.2O added to said suspension and agitate for preset time. At step 108, NaOH solution is added and stirred with resultant solution of step 106 to obtain pH 11. The method further includes, at step 110, the resultant solution of step 108 is heated for predetermined time and temperature. Finally, at step 112, the method includes, cooling the output nanoparticles of step 110 to room temperature, washing and filtering to obtain the sonocatalyst copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material.

(24) In one embodiment, the predetermined temperature for preparing copper sulfide (Cu.sub.2S) nanoparticle at step 102 is 220 C. The predetermined time for preparing copper sulfide (Cu.sub.2S) nanoparticle at step 102 is 0.5 h. Further, the Cu.sub.2S nanoparticle is sonicated in deionized water at step 104 for 1 h. In one embodiment, the predetermined quantity of Fe(NO.sub.3).sub.3. 9H.sub.2O and Co(NO.sub.3).sub.2. 6H.sub.2O is agitated with said suspension at step 106 for 1 h. In one embodiment, the resultant solution of step 108 is heated in an autoclave at 180 C. for 12 h. The autoclave could be a Teflon-lined stainless-steel autoclave.

(25) FIG. 2 exemplarily illustrates a method 200 of treating dye wastewater using said sonocatalyst (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite. In one embodiment, the method 200 of treating dye wastewater, comprising the steps of, pre-sonicating the dye wastewater with a sonocatalyst composition, at step 202. At step 204, the pre-sonicated solution is irradiated in presence of hydrogen peroxide (H.sub.2O.sub.2). The method 200 further includes, generating treated water after complete degradation of organic dye pollutants, at step 206.

(26) In some embodiments, the method is performed by using an ultrasonic irradiation process. The sonocatalyst composition is copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material. In one embodiment, the dye wastewater is pre-sonicated with the sonocatalyst composition in 35 to 40 kHz frequency and 100 W output power. In some embodiments, the dye is removed from the dye wastewater within 2 to 20 mins. Further, this ultrasound-assisted advanced oxidation process enables complete degradation of dyes including, methylene blue (MB), mRhodamine (RhB), and methyl orange (MO), in presence of H.sub.2O.sub.2 as a green oxidant after 2 mins.

(27) In one embodiment, the degradation efficiency of methylene blue (MB) through H.sub.2O.sub.2/ultrasonic irradiation, and ultrasonic irradiation/Cu.sub.2S/CoFe.sub.2O.sub.4 systems in 2 mins was 5% and 60%, respectively. In another embodiment, the combined use of ultrasonic irradiation, H.sub.2O.sub.2 and Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite enhanced the degradation efficiency of methylene blue (MB) from 68% to 100% within 2 mins. Herein, 4 mM concentration of hydrogen peroxide (H.sub.2O.sub.2) is used.

(28) In one embodiment, the sonocatalyst is recycled and reused. The nanocomposite could be magnetically separated and reused without any changes in its structure for several consecutive runs of sonocatalytic dye degradation process. Significant loss of activity is not observed up to four catalytic cycles, which indicates the stability of the sonocatalyst, and efficiency for the degradation of organic dyes from the wastewater or effluents. Further, the magnetic properties of the sonocatalyst nanocomposite allow easy retrieval of the catalyst from the reaction mixture for subsequent uses.

(29) By this invention, a novel, eco-friendly and economical method for the complete degradation of the organic dye pollutants from the industrial wastewater is achieved. Further, a novel magnetic copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material is synthesized rapidly in ease, with low energy consumption. Further, the semiconductor-based sonocatalysis could overcome the disadvantages of existing photocatalytic technology because, the ultrasonic (US) wave has a strong penetrating ability for any dye concentration of water medium. Further, the sonocatalyst has enough stability, as its structure and degradation ability does not change even after multiple use. After completion of the process, the sonocatalyst could be separated and reused from a waste water system, without any need for complex separation process using a magnet.

(30) The following examples are intended to illustrate certain embodiments of the present invention, but do not exemplify the full scope of the invention.

EXAMPLES

Example1: Synthesis of Sonocatalyst Composition

(31) Dye effluents discharged from many industries, like textile, are among the most adverse materials that should be removed and treated before entering to the surface waters and rivers. Different methods are used to remove such pollutants. Sonocatalysis process is one of the advanced oxidizing processes using a catalyst, which is an effective method for treating water. Herein, the catalyst or sonocatalyst is a new composite of Cu.sub.2S and ferrites that have a band gap, which enables degrading of dyes in presence of ultrasound and hydrogen peroxide (H.sub.2O.sub.2). Based on the displacement of band gap to the visible area, it proves an application in degrading organic dyes available in dye effluents. Copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) catalyst is a nanocomposite material characterized with magnetically recyclability characteristic for removing dye in presence of ultrasound.

(32) FIG. 3 exemplarily illustrates a laboratory synthesis process of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite for degrading high concentration of dye pollutants. In order to prepare Cu.sub.2S nanoparticles, 2 g of the Cu(II) diethyldithiocarbamate complex was placed in a porcelain crucible and then heated in an electric furnace at 22 C. for 0.5 h in air. For synthesizing the magnetic Cu.sub.2S/CoFe.sub.2O.sub.4 nanohybrid with uniform dispersion, 0.113 g of Cu.sub.2S nanoparticles was applied into 25 ml deionized water and sonicated for 1 h. Then, 0.43 g of Fe(NO.sub.3).sub.3.9H.sub.2O and 0.15 g of Co(NO.sub.3).sub.2.6H.sub.2O were added into the suspension and stirred for 1 h. After that, the mixture with pH of 11 obtained by adding NaOH solution (6 M) was re-stirred for 1 h and left in a 50 mL Teflon-lined stainless-steel autoclave for 12 h under auto-generated pressure at 180 C. Finally, it was cooled down to the room temperature and the final yield was filtered after washing with water.

Example2: Physical CharacterizationXRD Analysis

(33) XRD diffraction pattern of Cu.sub.2S/CoFe.sub.2O.sub.4 nanostructure are presented in FIG. 4. The XRD diffraction pattern exhibits diffraction peaks of both Cu.sub.2S and CoFe.sub.2O.sub.4. Diffraction peaks related to the impurities were not observed in the patterns, confirming the high purity of the synthesized product. The diffraction peaks were widened due to small size effect of the Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite.

Example3: FT-IR Spectrum Analysis

(34) By FT-IR spectroscopy, FT-IR spectrum of the Cu.sub.2S and CoFe.sub.2O.sub.4 nanocomposite was recorded. In FT-IR spectrum of the Cu.sub.2S nanoparticles as shown in FIG. 5, no band was observed due to the stretching and bending vibrations of (a) CuS appeared below 400 cm.sup.1. FIG. 5 shows the FT-IR spectrum of (b) pure CoFe.sub.2O.sub.4, which displayed two principal absorption bands below 1000 cm.sup.1, a characteristic feature of all ferrites. FIG. 5 shows the FT-IR spectrum of the (c) Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite, which displayed two main absorption bands below 1000 cm.sup.1. These bands could be related to the CoFe.sub.2O.sub.4 nanoparticles in the nanocomposite. XRD and FT-IR results confirms that the Cu.sub.2S/CoFe.sub.2O.sub.4 composite was synthesized hydrothermally completely and pure. Therefore, the morphology and structure of the product were surveyed using SEM. The SEM images show nanocomposite has cubes of Cu.sub.2S nanoparticles covered by CoFe.sub.2O.sub.4 nanoparticles, as shown in FIG. 6A and FIG. 6B.

Example4: X-Ray Spectroscopy Analysis

(35) Further investigation was carried out by energy dispersive X-ray spectroscopy (EDX) to characterize the elemental composition of the Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite. The presence of Fe, O, Co, Cu and S elements in the nanocomposite can be proved by the EDX elemental spectrum, as shown in FIG. 7A and the corresponding elemental mappings distribution in FIG. 7B shows the uniform distribution of these elements in the nanocomposite.

Example5: Vibrating Sample Magnetometer (VSM) Analysis

(36) The magnetic properties of the pure CoFe.sub.2O.sub.4 nanoparticles and Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite were studied by vibrating sample magnetometer (VSM) at room temperature. As shown in FIG. 8A and FIG. 8B, the nanocomposite displayed a ferromagnetic behavior. The nanocomposite of Cu.sub.2S/CoFe.sub.2O.sub.4 gives the coercive force (H.sub.c), saturation magnetization (M.sub.s) and remnant magnetization (M.sub.r) of 480 Oe, 36.26 emu/g and 9.85 emu/g, respectively. These values were less than that of pure CoFe.sub.2O.sub.4 (Hc: 898.26 Oe, Ms: 62.78 emu/g and Mr: 25.9 emu/g). However, Hc, Ms and Mr values of Cu.sub.2S/CoFe.sub.2O.sub.4 were less than those of CoFe.sub.2O.sub.4 due to the presence of non-magnetic Cu.sub.2S.

Example6: Absorption Spectroscopy Analysis

(37) FIG. 9 shows the absorption spectrum of the Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite dispersed in distilled water. This spectrum exhibits defined absorption edge at 630 nm, corresponding to energy gap of 1.96 for the Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite.

Example7: Treatment of Dye Wastewater

(38) Degradation of dyes in aqueous solutions was investigated in the presence of the Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite using ultrasonic bath. In a typical manner, 50 ml of methylene blue (MB) solution with initial concentration of 25 mg/L containing 25 mg sonocatalyst was sonicated with a frequency of 37 kHz and 100 (W) output power. Before ultrasonic irradiation, the above solution was stirred for 30 min in the dark to achieve adsorption-desorption equilibrium between the dye and sonocatalyst. Then, it was ultrasonic irradiated in the presence of H.sub.2O.sub.2 (4 mM). FIG. 10 shows the UV-Vis absorbance and color changes of MB aqueous solution in the presence of the Cu.sub.2S/CoFe.sub.2O.sub.4 and H.sub.2O.sub.2 under ultrasonic irradiation. From the figure, the intensity of absorption band at 664 nm decreased and disappeared within 2 min.

(39) The efficiency of ultrasonic irradiation, Cu.sub.2S/CoFe.sub.2O.sub.4/H.sub.2O.sub.2, H.sub.2O.sub.2/ultrasonic irradiation and Cu.sub.2S/CoFe.sub.2O.sub.4/ultrasonic irradiation systems for degradation of MB were evaluated in control experiments. The ability of ultrasonic irradiation alone and Cu.sub.2S/CoFe.sub.2O.sub.4/H.sub.2O.sub.2 system for degrading MB within 2 min were negligible. However, the degradation efficiency of MB through H.sub.2O.sub.2/ultrasonic irradiation and ultrasonic irradiation/Cu.sub.2S/CoFe.sub.2O.sub.4 systems with 2 min was 5% and 60%, respectively. The above results confirmed that the combined use of ultrasonic irradiation, H.sub.2O.sub.2 and Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite is necessary to achieve fast and complete degradation of the dyes.

(40) To obtain the optimum concentration of H.sub.2O.sub.2 for degradation of MB in Cu.sub.2S/CoFe.sub.2O.sub.4/H.sub.2O.sub.2/ultrasonic irradiation process, six scenarios were developed and tested with different concentrations of H.sub.2O.sub.2 varying from 0 to 5 mM. Based on the results depicted in FIG. 11, 60% of MB was removed in the absence of H.sub.2O.sub.2 within 2 mins. By enhancing the concentration of H.sub.2O.sub.2 in the ultrasound degradation experiments from 1 to 4 mM, the MB removal efficiency was enhanced from 68% to 100% within 2 mins. Herein, 4 mM was chosen as the optimum concentration of H.sub.2O.sub.2 for degradation.

(41) Subsequently, the degradation of other organic dyes in aqueous solution including MO and Rhodamine B (RhB) was also studied to verify the generality of the sonocatalytic system using the synthesized Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite. As observed from FIG. 12, complete degradation (100%) of both RhB and MO was achieved within 8 and 18 min. From the results, the sonocatalyst acted differently in sonocatalytic degradation of the studied dyes, mainly due to their different chemical structure, sizes, compositions and electric charges.

Example8: Sonocatalytic Degradation Mechanism

(42) Basically, ultrasonic irradiation forms high wavelength light that excites the catalyst to generate electron-hole pairs and hydroxyl radicals on its surface according to the sonoluminescence mechanism. Collapsing cavity bubbles in the solution creates high-temperature hot spots that accelerate the pyrolysis of H.sub.2O.sub.2 to produce hydroxyl radicals (.OH) on the surface of the catalyst. Similar to light, hot spots and their heat energies could also excite the Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite. The conduction band (CB) and valence band (VB) potentials of Cu.sub.2S and CoFe.sub.2O.sub.4 were calculated for band structure perception of Cu.sub.2S/CoFe.sub.2O.sub.4 nanocomposite using the following equation:
EVB=XE.sub.e+0.5E.sub.g
ECB=EVBE.sub.g

(43) E.sub.e is the energy of free electrons on the hydrogen scale (4.5 eV), X is the electronegativity of the semiconductor, E.sub.g is the band gap energy of the semiconductor, EVB and ECB are the valance and conduction potentials. Since, the absolute electronegativity of Cu.sub.2S is 4.99 eV, then its VB and CB were calculated 1.59 and 0.61 eV, respectively. Furthermore, for the absolute electronegativity of CoFe.sub.2O.sub.4 (5.47 eV), VB and CB were respectively calculated (1.93 eV and 0.01 eV). In an instance, Cu.sub.2S has more negative CB potential than CoFe.sub.2O.sub.4, therefore, the injection of excited-state electrons in CB of Cu.sub.2S into CB of CoFe.sub.2O.sub.4 could be occurred under the influence of the generated light and heat. In another instance, the VB potential of CoFe.sub.2O.sub.4 (EVB=1.93 eV) is more positive than the VB potential of Cu.sub.2S (EVB=1.59 eV), indicating that the photogenerated holes on the CoFe.sub.2O.sub.4 could transfer into VB of Cu.sub.2S and then oxidize OH.sup. into .OH, as shown in FIG. 13. Concurrently, the sonogenerated holes in valance band (VB) of CoFe.sub.2O.sub.4 could be easily transferred to the VB of Cu.sub.2S and oxidize OH (or H.sub.2O.sub.2 molecules) adsorbed on the surface of Cu.sub.2S particles to form .OH, as shown in FIG. 13. The .OH radicals show strong oxidation activity participating in the sonodegradation reactions. Also, some of holes maybe directly involved in the oxidation of methylene blue (MB) to produce unstable MB.sup.+ as a target of OH.sup. attack leading to MB..sup.+ as a better target for .OH.
H.sup.++OH.OH(4)
MB.sup.+h.sup.+MB.sup.+(unstable)(5)
MB..sup.++.OH CO.sub.2+H.sub.2O(6)

(44) On the other hand, the produced hydroxyl radicals (.OH) resulting from reaction of the electrons in CB with H.sub.2O.sub.2 were active enough to degrade MB to the innocent products (CO.sub.2, H.sub.2O. etc.). The simplified mechanism of MB sonocatalytic degradation over Cu.sub.2S/CoFe.sub.2O.sub.4 sonocatalyst is illustrated in FIG. 13. The reusability of the sonocatalytic was also tested upon the separation of the sonocatalyst magnetically and then performance of the sonocatalysis for multiple cycles, as shown in FIG. 14. Any significant loss of activity is not observed up to four catalytic cycles, which indicated that as-prepared magnetic sonocatalyst was stable and very effective for the degradation of organic dyes from water.

(45) One aspect of the present disclosure is directed to a composition for treating dye wastewater, comprising a copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material. In one embodiment, the composition further comprises hydrogen peroxide (H.sub.2O.sub.2). In a related embodiment, the concentration of hydrogen peroxide (H.sub.2O.sub.2) ranges from 0 mM to 5 mM. In another related embodiment, the optimum concentration of hydrogen peroxide (H.sub.2O.sub.2) is 4 mM. In one embodiment, the coercive force (H.sub.c) of the nanocomposite material is 480 Oe. In another embodiment, the saturation magnetization (M.sub.s) of the nanocomposite material is 36.26 emu/g. In one embodiment, the remnant magnetization (M.sub.r) of the nanocomposite material is 9.85 emu/g. In one embodiment, said nanocomposite material is a sonocatalyst.

(46) Another aspect of the present disclosure is directed to a method of synthesizing a composition for treating dye wastewater, comprising the step of: a) preparing copper sulfide (Cu.sub.2S) nanoparticle by heating Cu(II) diethyldithiocarbamate complex at predetermined time and temperature; b) adding Cu.sub.2S nanoparticle in deionized water and sonicating them together for preset time to form a suspension; c) adding predetermined quantity of Fe(NO.sub.3).sub.3. 9H.sub.2O and Co(NO.sub.3).sub.2. 6H.sub.2O to said suspension and agitate for preset time; d) adding NaOH solution and stir with resultant solution of step (c) to obtain pH 11; e) heating the resultant solution of step (d) for predetermined time and temperature, and f) cooling the output nanoparticles of step (e) to room temperature, washing and filtering to obtain the sonocatalyst copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material.

(47) In one embodiment, the predetermined temperature for preparing copper sulfide (Cu.sub.2S) nanoparticle at step (a) is 220 C. In another embodiment, the predetermined time for preparing copper sulfide (Cu.sub.2S) nanoparticle at step (a) is 0.5 h. In one embodiment, the Cu.sub.2S nanoparticle is sonicated in deionized water at step (b) for 1 h. In another embodiment, the predetermined quantity of Fe(NO.sub.3).sub.3. 9H.sub.2O and Co(NO.sub.3).sub.2. 6H.sub.2O is agitated with said suspension at step (c) for 1 h. In one embodiment, the resultant solution of step (d) is heated in autoclave at 180 C. for 12 h.

(48) Another aspect of the present disclosure is directed to a method of treating dye wastewater, comprising the steps of: (a) pre-sonicating the dye wastewater with a sonocatalyst composition; (b) irradiating the pre-sonicated solution in presence of hydrogen peroxide (H.sub.2O.sub.2), and (c) generating treated water on removal of dye. In one embodiment, the method is an ultrasonic irradiation process. In another embodiment, the sonocatalyst composition is copper sulfide and cobalt ferrite (Cu.sub.2S/CoFe.sub.2O.sub.4) nanocomposite material. In one embodiment, the dye wastewater is pre-sonicated with the sonocatalyst composition in 35 to 40 kHz frequency and 100 W output power. In another embodiment, the dye is removed within 2 to 20 mins. In one embodiment, the sonocatalyst composition is recycled and reused.

(49) The foregoing description comprise illustrative embodiments of the present invention. Having thus described exemplary embodiments of the present invention, it should be noted by those skilled in the art that the within disclosures are exemplary only, and that various other alternatives, adaptations, and modifications may be made within the scope of the present invention. Merely listing or numbering the steps of a method in a certain order does not constitute any limitation on the order of the steps of that method.

(50) Many modifications and other embodiments of the invention will come to mind to one skilled in the art to which this invention pertains having the benefit of the teachings presented in the foregoing descriptions. Although specific terms may be employed herein, they are used only in generic and descriptive sense and not for purposes of limitation. Accordingly, the present invention is not limited to the specific embodiments illustrated herein. While the above is a complete description of the preferred embodiments of the invention, various alternatives, modifications, and equivalents may be used. Therefore, the above description and the examples should not be taken as limiting the scope of the invention, which is defined by the appended claims.