Refractory organic pollutants have become the focus and difficulty for research workers with high stability and strong toxicity,which cannot be treated by traditional biochemical methods.In contrast,Advanced Oxidation Process?AOP?is considered as a promising technology that can generate highly active free radicals and completely mineralize organic pollutants into water and carbon dioxide.Fenton oxidation technology is a kind of AOPs.The traditional Fenton oxidation technology uses Fe2+as a catalyst for homogeneous Fenton catalysis,however,it has the disadvantages of narrow p H response range and difficult recovery of iron ions.Heterogeneous Fenton-like catalysis overcomes the shortcomings of traditional homogeneous Fenton catalysis and exhibits excellent catalytic activity.In this paper,Rhodamine B was used as a simulated organic pollutant to investigate the Fenton-like catalytic performance on g-C3N4-based material.XRD,FTIR,SEM and XPS were used to characterize the synthesized catalyst.Graphitized carbon nitride?g-C3N4?is a typical inorganic non-metallic material,which attracts huge concern mainly as a photocatalyst,but its Fenton-like catalytic performance has been overlooked.In the third chapter of this paper,metal-free catalyst g-C3N4was synthesized by conventional urea pyrolysis without any modification,and then the Fenton-like catalytic performance of g-C3N4was evaluated for the first time by degrading Rhodamine B over a wide p H range.The results showed that the g-C3N4was an efficient metal-free heterogeneous Fenton-like catalyst.The highest activity occurred under a weakly alkaline condition of about p H10.The experiment of catalyst recycling indicated that g-C3N4had long-term stability.The reactive oxidizing species of·OH,generated by the g-C3N4activating H2O2,was identified by ESR and further supported by a scavenging experiment of·OH using isopropanol as the scavenger.The HNO3oxidation of g-C3N4resulted in catalytic deactivation,implying the catalytic activity originated from the surface reduced groups of g-C3N4.The structure of synthesized g-C3N4before and after the HNO3oxidation was characterized by XRD,FTIR,XPS,and a possible catalytic mechanism was proposed.In the fourth chapter of this paper,a small amount of Cu2+was introduced into the g-C3N4heterogeneous Fenton-like system.The results showed that Cu2+and g-C3N4had obvious synergistic effect.Under the concentration of Cu2+was 0.64mg/L,The results showed that the Cu2+/g-C3N4system exhibited excellent Fenton-like catalytic performance for a variety of dyes over a wide p H range.The content of Cu2+in the supernatant was determined by flame atomic absorption spectrometry after absorption-desorption equilibrium.The result showed that the Cu2+content decreased significantly,and the reduced Cu2+may be adsorbed to the active site of g-C3N4.Nitric acid oxidation experiments proved that the reducing active sites in the g-C3N4structure played an important role in the catalytic process of the Cu2+/g-C3N4system.Low concentration of Cu2+was also necessary in the catalytic process of Cu2+/g-C3N4system.EPR experiments and the radical trapping experiments showed that·OH radicals were the major reactive oxidizing species in the reaction process,During the catalytic reaction,g-C3N4provides reducing active sites for the Cu+/Cu2+redox cycle,and promotes Fenton-like catalytic processes through strong electronic interactions.In the fifth chapter of this paper,Cu@g-C3N4composite was prepared by one-step hydrothermal method.Cu2+was existed in the form of Cu?II?-N?copper porphyrin?in Cu@g-C3N4composite.Cu@g-C3N4composite exhibited excellent catalytic performance at room temperature?25°C?and p H5.Rhodamine B degradation rate reached 90.3%after 60 min catalytic reaction.The apparent activation energy of degradation calculated was 7.09 k J/mol,implying a lower reaction barrier.The radical trapping experiments proved that·OH radicals were the major reactive oxidizing species.The electron-donating effect of N made the reduction product[Cu-N]+more stable than Cu+,which is beneficial to the redox reaction of Cu+. |