Sulfonamide antibiotics(SAs)are still widely used as the first broad-spectrum antibiotics used in clinical practice.Among them,sulfamethoxazole(SMX)and sulfisoxazole(SIM)are common human antibiotics,while sulfadiazine(SDZ)is a commonly used veterinary antibiotic.SAs can be discharged into water bodies through several routes,resulting in SAs concentrations in water ranging between ng/L andμg/L.Therefore,it is necessary to remove SAs from wastewater before discharge to natural water bodies.Non-homogeneous photofenton technology,due to its high efficiency,low iron sludge and good reusability,has been widely used for the removal of refractory organic pollutants.However,the photo-Fenton catalysts are difficult to be recycled from the reaction system.MOFs are metal-organic skeletons constructed by metal nodes and organic ligands,which have the advantages of ultra-high specific surface area,diverse structures,tunable morphology and abundant active sites.In this work,MIL-100(Fe)sulfide was derived from magnetic Fe3S4,while retaining part of the advantages of its MOF precursor and Fe3S4.The derived material Fe3S4 is easily recyclable as an excellent narrow bandgap ferromagnetic semiconductor after the reaction,and the abundant reduction sites on the surface can activate H2O2 to produce·OH for degradation of organic pollutants.From these aspects,photo-Fenton with Fe3S4 as catalyst may have great potential for development.The main work of this thesis is as follows.(1)The magnetic Fe3S4 was prepared by hydrothermal synthesis of MIL-100(Fe)and derivatization of MIL-100(Fe)using thioacetamide sulfide.The successful preparation of the material was demonstrated by powder X-ray diffraction characterization.The method of derivatizing Fe3S4 using MOF as a template has several advantages over other conventional methods in the literature:Firstly,MIL-100(Fe)is easy to prepare and does not require high sulfidation conditions,so it is relatively convenient to derive high-quality Fe3S4.Secondly,since MIL-100(Fe)is used as a template,the synthesized Fe3S4 can inherit the advantages of MIL-100(Fe),so that Fe3S4 has a relatively large specific surface area.Meanwhile,many active sites were exposed in the process of derivatization of Fe3S4.(2)The precursor MIL-100(Fe)and the derived metal sulfide Fe3S4 were characterized by scanning electron microscope,transmission electron microscope,high power transmission electron microscope,magnetic hysteresis loop,ultraviolet-visible diffuse reflectance spectroscopy,electrochemistry and X-ray photoelectron spectroscopy.It was demonstrated that MIL-100(Fe)successfully derived magnetic Fe3S4.The morphology of Fe3S4 prepared by derivatization was regular flower-like microspheres with good magnetic properties that could be easily separated and recovered from aqueous solution.In addition,Fe3S4 has excellent light absorption performance and can utilize both UV and visible light,so that different light sources can be selected in the future according to the actual environment.(3)Testing the performance of derivative Fe3S4 photo-Fenton for SMX degradation under light conditions.Efficient degradation of mixed sulfonamide antibiotics was achieved by photo-Fenton under visible light.In this paper,environmental factors affecting SMX degradation,recyclability of materials,SMX degradation mechanism and possible degradation pathways were systematically investigated.The results show that the Fe3S4/H2O2/vis system can degrade 100%of SMX within 10 min.Also,given the excellent photo responsiveness of Fe3S4,it can efficiently degrade SMX from UV to visible light and from real sunlight to light sources of different wavelengths.In this work,the detailed exploration of p H,catalyst dosage,H2O2 concentration and inorganic anion.The effects of p H,catalyst dosage,H2O2 concentration and inorganic anion on the degradation performance,cycling performance in aqueous solution and performance under real sunlight and different wavelength light sources were explored in detail in this work.The main reactive oxygen species(ROS)in the Fe3S4/H2O2/vis system were inferred to be·OH and 1O2 by capture experiments and electron spin resonance spectroscopy characterization techniques.X-ray photoelectron spectroscopy,instantaneous photocurrent,and impedance spectroscopy were also used to study the photo-Fenton reaction mechanism.Based on UHPLC-MS analysis,the degradation pathways of SMX,SIM and SDZ were proposed. |