Fenton and Fenton-like processes,which could produce highly reactive species to degrade organic contaminants,have been widely used in the field of wastewater treatment.Therein,the chemistry of Fenton process including...Fenton and Fenton-like processes,which could produce highly reactive species to degrade organic contaminants,have been widely used in the field of wastewater treatment.Therein,the chemistry of Fenton process including the nature of active oxidants,the complicated reactions involved,and the behind reason for its strongly pH-dependent performance,is the basis for the application of Fenton and Fenton-like processes in wastewater treatment.Nevertheless,the conflicting views still exist about the mechanism of the Fenton process.For instance,reaching a unanimous consensus on the nature of active oxidants(hydroxyl radical or tetravalent iron)in this process remains challenging.This review comprehensively examined the mechanism of the Fenton process including the debate on the nature of active oxidants,reactions involved in the Fenton process,and the behind reason for the pH-dependent degradation of contaminants in the Fenton process.Then,we summarized several strategies that promote the Fe(Ⅱ)/Fe(Ⅲ)cycle,reduce the competitive consumption of active oxidants by side reactions,and replace the Fenton reagent,thus improving the performance of the Fenton process.Furthermore,advances for the future were proposed including the demand for the high-accuracy identification of active oxidants and taking advantages of the characteristic of target contaminants during the degradation of contaminants by the Fenton process.展开更多
In this paper it is presented the results of advanced oxidation of leachates from a technified sanitary landfill located in the State of Querétaro, Mexico. One characteristic of already stabilized leachates from ...In this paper it is presented the results of advanced oxidation of leachates from a technified sanitary landfill located in the State of Querétaro, Mexico. One characteristic of already stabilized leachates from sanitary landfills like this case, is their difficult degradation, mainly because the organic matter contained is recalcitrant. For the samples collect, four sites were selected, where three points per site were sampled, measuring at each site the parameters: temperature, pH, conductivity, redox potential (ORP) and dissolved oxygen (DO) and leachate samples were collected. On the other hand, the Chemical Oxygen Demand (COD) of crude leachates, leachates acidified and leachates oxidized by Fenton reagent and Ozone-UV combined were analyzed. COD was used to monitor the degradation kinetics. With the results, the ArcGIS software was applied to study the distribution of temperature, dissolved oxygen and COD mainly in the leachate lagoon. For the application of Fenton reagent in the crude leachate oxidation, the pH was first adjusted and Fe<sup>2+</sup>/H<sub>2</sub>O<sub>2</sub> ratio was optimized. The efficiency of Ozone-UV treatments was studied through COD degradation kinetics. The graphs of in (Ci/Co) vs time, showed that the kinetic processes are of order one, with very acceptable regression coefficients (R<sup>2</sup>) and extraordinarily similar speed constants (K). With Fenton oxidation, the highest percentage of COD degradation was achieved and with Ozone-UV oxidation, it was possible to practically degrade all the COD.展开更多
采用UV-Fenton技术光催化氧化高浓度邻苯二甲酸二辛酯(DOP)生产废水,确定最佳操作条件为:初始pH=3.8,H2O2浓度为9.99 g/L,H2O2/Fe2+摩尔比为20∶1,光照反应60 m in。此条件下的废水COD去除率为89.1%,出水COD值在570 mg/L左右。经正交试...采用UV-Fenton技术光催化氧化高浓度邻苯二甲酸二辛酯(DOP)生产废水,确定最佳操作条件为:初始pH=3.8,H2O2浓度为9.99 g/L,H2O2/Fe2+摩尔比为20∶1,光照反应60 m in。此条件下的废水COD去除率为89.1%,出水COD值在570 mg/L左右。经正交试验确定影响处理效果各因素的重要性顺序为:H2O2浓度>H2O2/Fe2+摩尔比>光照反应时间>pH。UV的加入与单独的Fenton体系存在正相关的协同作用。废水降解的表观过程符合一级反应动力学模式。展开更多
基金supported by the National Natural Science Foundation of China(Nos.22206050 and 52270047).
文摘Fenton and Fenton-like processes,which could produce highly reactive species to degrade organic contaminants,have been widely used in the field of wastewater treatment.Therein,the chemistry of Fenton process including the nature of active oxidants,the complicated reactions involved,and the behind reason for its strongly pH-dependent performance,is the basis for the application of Fenton and Fenton-like processes in wastewater treatment.Nevertheless,the conflicting views still exist about the mechanism of the Fenton process.For instance,reaching a unanimous consensus on the nature of active oxidants(hydroxyl radical or tetravalent iron)in this process remains challenging.This review comprehensively examined the mechanism of the Fenton process including the debate on the nature of active oxidants,reactions involved in the Fenton process,and the behind reason for the pH-dependent degradation of contaminants in the Fenton process.Then,we summarized several strategies that promote the Fe(Ⅱ)/Fe(Ⅲ)cycle,reduce the competitive consumption of active oxidants by side reactions,and replace the Fenton reagent,thus improving the performance of the Fenton process.Furthermore,advances for the future were proposed including the demand for the high-accuracy identification of active oxidants and taking advantages of the characteristic of target contaminants during the degradation of contaminants by the Fenton process.
文摘In this paper it is presented the results of advanced oxidation of leachates from a technified sanitary landfill located in the State of Querétaro, Mexico. One characteristic of already stabilized leachates from sanitary landfills like this case, is their difficult degradation, mainly because the organic matter contained is recalcitrant. For the samples collect, four sites were selected, where three points per site were sampled, measuring at each site the parameters: temperature, pH, conductivity, redox potential (ORP) and dissolved oxygen (DO) and leachate samples were collected. On the other hand, the Chemical Oxygen Demand (COD) of crude leachates, leachates acidified and leachates oxidized by Fenton reagent and Ozone-UV combined were analyzed. COD was used to monitor the degradation kinetics. With the results, the ArcGIS software was applied to study the distribution of temperature, dissolved oxygen and COD mainly in the leachate lagoon. For the application of Fenton reagent in the crude leachate oxidation, the pH was first adjusted and Fe<sup>2+</sup>/H<sub>2</sub>O<sub>2</sub> ratio was optimized. The efficiency of Ozone-UV treatments was studied through COD degradation kinetics. The graphs of in (Ci/Co) vs time, showed that the kinetic processes are of order one, with very acceptable regression coefficients (R<sup>2</sup>) and extraordinarily similar speed constants (K). With Fenton oxidation, the highest percentage of COD degradation was achieved and with Ozone-UV oxidation, it was possible to practically degrade all the COD.
文摘采用UV-Fenton技术光催化氧化高浓度邻苯二甲酸二辛酯(DOP)生产废水,确定最佳操作条件为:初始pH=3.8,H2O2浓度为9.99 g/L,H2O2/Fe2+摩尔比为20∶1,光照反应60 m in。此条件下的废水COD去除率为89.1%,出水COD值在570 mg/L左右。经正交试验确定影响处理效果各因素的重要性顺序为:H2O2浓度>H2O2/Fe2+摩尔比>光照反应时间>pH。UV的加入与单独的Fenton体系存在正相关的协同作用。废水降解的表观过程符合一级反应动力学模式。
文摘目的研究UV/Fenton氧化法对难降解有机物硝基苯的氧化能力,确定UV/Fenton氧化法处理硝基苯处理废水的工艺条件.方法以自配硝基苯水样为处理对象,采用自制光反应器,通过试验研究分析H2O2投加量、Fe2+质量浓度、反应时间、pH值、硝基苯初始质量浓度等对UV/Fenton氧化法处理硝基苯废水处理效果的影响.结果实验研究结果表明,UV/Fenton氧化法对硝基苯有较高的去除率和反应速率,硝基苯的去除率可达到95%.H2O2投加量、Fe2+质量浓度、反应时间、pH值和硝基苯初始质量浓度对处理效果均有较大影响.结论硝基苯的质量浓度在不大于200mg/L时,UV/Fenton法能够有效去除硝基苯,最佳反应条件为:H2O2倍数为1.5左右,Fe2+与H2O2的摩尔比为1∶30,pH值为4左右,反应时间为50 min.
