| Landfill leachate,as a kind of high-concentration organic wastewater that is difficult to be treated,has become an urgent problem to be solved due to its complex composition,poor biodegradability and high pollutant concentration.Therefore,it is necessary to find more appropriate treatment technology for its in-depth treatment.In this study,the biochemical tail water of landfill leachate was treated by coagulation-persulfate catalytic oxidation.The single factor experiment was carried out to optimize the treatment process and evaluate the coagulation removal effect of various coagulants on the organic matter in the biochemical tail water.On this basis,Cu/Mn bimetallic supported activated carbon was prepared to catalyze the persulfate oxidation and further remove the organic matter in the coagulated effluent.The changes of organic compounds before and after the reaction were analyzed by UV-VIS and 3D-EEM.The results showed that:(1)the coagulant effect of iron coagulant on biochemical tail water of leachate was obviously better than that of aluminum coagulant,and ferric chloride(FC)was determined as the best coagulant.For the coagulation treatment of biochemical tail water of landfill leachate,the optimal dosage of FC is 800 mg/L without additional adjustment of p H,and the optimal dosage of polyacrylamide(PAM)is 200 mg/L.At this time,the removal rates of CODCr,UV254 and chroma are 57.5%,74.8%and 95.2%,respectively.The residual CODCr value was 469.7 mg/L.(2)The persulfate oxidation reaction is greatly affected by temperature.When the reaction temperature is lower than 60℃,persulfate basically does not decompose to produce sulfate radical and react with organic matter in the biochemical tail water of landfill leachate.Under the optimal reaction condition,that is,the reaction temperature is 90℃,the CODCrremoval rate of Na2S2O8 and K2S2O8 system can reach 94%within 30 min,and the residual CODCr value is only 36.7 mg/L.(3)Cu/Mn bimetallic supported activated carbon material was effectively prepared.According to the influence of metal type and metal load on persulfate catalytic activation,Cu-KMn/AC was selected as the best catalyst for persulfate system.Secondly,through single factor study,obtained the optimal dosage of Na2S2O8,K2S2O8 with Cu/Mn bimetallic supported activated carbon catalyst is 6 g/L,7g/L and 4g/L,respectively,under the optimal experimental conditions of reaction temperature of 50℃,reaction time of 90 min,without adjusting p H.In Na2S2O8 and K2S2O8 systems,the CODCr removal rate and residual CODCrvalues were 83.2%,83.4%,93.0 mg/L and 99.7 mg/L,respectively.Under the same reaction conditions,KHSO5 dosage of 15 g/L was added for 4 h.The CODCr removal rate and residual CODCr values in KHSO5 system were 81.9%and 90.6 mg/L,respectively.(4)The analysis of UV-VIS and 3D-EEM showed that the aromatization degree,molecular weight and polymerization degree of organic matter decreased in the biochemical tail water of landfill leachate after treatment,DOM aromaticity was weakened,the aromatic ring structure in the biochemical tail water was reduced,and organic matter such as humic acid and fuluric acid were effectively degraded after oxidation by sulfate system.It can be concluded that the persulfate catalytic oxidation system can oxidize or even mineralize most organic matter,and can degradeπ-π*and most benzene ring organic matter with conjugate system.(5)In this study,a feasible coagulation-persulfate catalytic oxidation process of landfill percolation biochemical tail water was explored with a new idea,which provided a new idea and theoretical basis for the technical optimization of the relevant treatment process of leachate. |