Aming at the serious water pollution problem,photocatalysis is an environmental method with the properties of high efficiency and no secondary pollution.In this paper,based on Ag Br,three visible light responsive photocatalysts was designed by constructing heterojunction.The separation rate of photogenerated carriers was promoted.Ag Br/Ce O2,Ag Br/Bi2S3,Ag2S/Zn In2S4 exhibited an good photocatalytic performances for degrading rhodamine B(Rh B),methyl orange(MO),tetracycline(TC),inhibiting the growth of Escherichia coli(E.coli),and decomposing water to produce hydrogen.It also played a role in that photocatalysis was involved in the treatment of fracturing flowback fluid.(1)Flower-like CeO2 was prepared via the ice-bath coprecipitation method,which could provide the big contact interface.Then Z-scheme Ag Br/Ce O2 heterojunction photocatalysts were synthesized via a facile deposition–precipitation method.The Ag Br mass fraction in the composites were altered,40 wt%-Ag Br/Ce O2 exhibited optimal photocatalytic activity.Following visible light irradiation for 180 min,the degradation rates of Rh B and MO by 40 wt%-Ag Br/Ce O2reached 96%and 93.4%,respectively.And99.7%E.coli disinfection was achieved in the presence of this photocatalyst.Under the visible light irradiation for 120 min,the degradation rate of TC was 77.8%.Due to the formation of Z-scheme heterojunction,40 wt%-Ag Br/Ce O2 possessed abundant Ce3+and oxygen vacancies,higher redox capacity and separation efficiency of photogenerated charge carriers..O2-,.OH,and h+played important roles in the photocatalytic process.(2)Flower-like Bi2S3 was prepared by a hydrothermal method,then the Z-scheme AgBr/Bi2S3 heterojunction photocatalyst was prepared by a facile deposition-precipitation method,and the Ag Br mass fraction in the composites was altered,90 wt%-Ag Br/Bi2S3 presented optimal photocatalytic property.Under the visible light illumination for 80 min,the removal rate of Rh B by 90 wt%-Ag Br/Bi2S3 was 98.93%;Under the illumination for 120 min,the removal rate of TC was 60.52%;Under the illumination for 180 min,the bacteriostatic rate of E.coli was 99.9%.On account of the formation of Z-scheme heterojunction,90 wt%-Ag Br/Bi2S3 performed higher redox capacity and separation efficiency of photogenerated charge carriers,.O2-,.OH,and h+played major roles in photocatalytic process.(3)Flower-like ZnIn2S4 was prepared by a hydrothermal method,type I-scheme Ag2S/ZnIn2S4was prepared by a ultrasonic method with Ag Br and Zn In2S4,Ag2S/Zn In2S4-1 was prepared by adding 1 wt%Ag Br,which performed the best photocatalytic property of hydrogen evolution.Under the irradiation of visible light for 4h,the hydrogen production of Ag2S/Zn In2S4-1 was 468.7μmol by loading 1 wt%H2Pt Cl6cocatalyst,and the hydrogen evolution rate was 2343.5μmol/h/g.Under the visible light irradiation for 120 min,the degradation rate of TC was 89.8%.After the formation of type I heterojunction,the bigger specific surface area and higher separation rate of photogenerated charge carriers enhanced the photocatalytic performance for Ag2S/Zn In2S4-1.(4)40 wt%-Ag Br/CeO2,90 wt%-Ag Br/Bi2S3,Ag2S/ZnIn2S4-1 were used for the treatment of fracturing flowback fluid.Combining fenton oxidation,catalytic ozonation and photocatalysis to treat the laboratory self-made fracturing fluid,the COD removal rate could reached up to 87.6%.Flocculation-fenton oxidation+adsorption-catalytic ozonation-photocatalysis were used together to treat the fracturing flowback fluid from Qinghai oilfield,The COD removal rate was 94.4%,the TOC was reduced by 87%,respectively.The contents of harmful components decreased obviously.After the treatments,the water quality all reached the standard of reusing,Ag2S/Zn In2S4-1 showed the best photocatalytic activity,.O2-、h+、e-played major roles in the photocatalysis treatment of fracturing flowback fluid. |