池勇志1,2,
赵建海1,2,
田秉晖3,
付翠莲1,4,
郑先强5
1.天津城建大学环境与市政工程学院天津市水质科学与技术重点实验室,天津 30038
2.天津城建大学基础设施防护和环境绿色生物技术国际联合研究中心,天津 30038
3.中国科学院生态环境研究中心环境水质学国家重点实验室,北京 10008
4.天津城建大学建筑设计研究院,天津 30038
5.天津天一爱拓科技有限公司,天津 30038
基金项目: 天津市科技计划项目(16YFXTSF00390)
天津市科技计划项目(15ZCZDSF00150)
天津城建大学科技成果转化奖励专项资金项目(KZZH2-A2-1726)
Mechanism and effect of pH on coating wastewater in neutralization and precipitation process
FU Haijuan1,2,,CHI Yongzhi1,2,
ZHAO Jianhai1,2,
TIAN Binghui3,
FU Cuilian1,4,
ZHENG Xianqiang5
1.Tianjin Key Laboratory of Water Quality Science and Technology, School of Environmental and Municipal Engineering, Tianjin Chengjian University, Tianjin 300384,Chin
2.Joint Research Centre for Protective Infrastructure Technology and Environmental Green Bioprocess, Tianjin Chengjian University, Tianjin 300384, Chin
3.State Key Laboratory of Environmental Aquatic Chemistry, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, Chin
4.Architectural Design and Research Institute, Tianjin Chengjian University, Tianjin 300384, Chin
5.Tianjin Tisun Itasca Technology Co.Ltd., Tianjin 300384, Chin
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摘要:采用中和沉淀法对涂装废水进行处理,研究了pH(4~12)对废水中总磷、COD、浊度、总铁、总镍、总锰等12种主要污染物去除率的影响,并结合絮体粒度分布、Zeta电位、絮体形貌和XRD图谱等表征方式对COD和重金属的去除机理进行了分析。研究结果表明,在综合考虑后续生化处理需要和处理成本的条件下,中和沉淀法处理涂装废水的适宜pH为8,废水经处理后所有重金属离子浓度和总磷浓度均达到《污水排入城镇下水道水质标准》 (GB/T 31962-2015 )B级标准,COD、浊度和氨氮的去除率分别为30.05%、46.51%和72.49%。无机污染物去除的主要途径包括磷酸盐沉淀形成、氢氧化物沉淀形成和吸附絮凝作用。COD的去除机制随着pH的变化而不同,在pH =2.18~8时,COD的去除主要由于不溶性金属络合物的形成、电性中和与卷扫网捕,在pH =10~12时,主要的作用机制为氢氧化物絮体对其的吸附作用和卷扫网捕。这对中和沉淀法工艺处理实际涂装废水有重要的指导意义。
关键词: 涂装废水/
中和沉淀法/
重金属/
去除率/
絮体形貌/
反应机理
Abstract:The neutralization and precipitation process was used for coating wastewater treatment, the effects of pH (4 to 12) on the removal efficiencies of 12 major pollutants such as total phosphorus, COD, turbidity, total iron, total nickel and total manganese were studied and the removal mechanisms of COD and heavy metals were analyzed with the floc size distribution, Zeta potential, the morphology of flocs and XRD patterns. The results showed that suitable pH was 8 for treatment of coating wastewater by neutralization and precipitation process. After the wastewater was treated by the process, the concentration of all heavy metal ions and total phosphorus in the wastewater could meet the class B standard of Wastewater Quality of Standards for Discharge to Municipal Sewers (GB/T 31962-2015). At pH=8, the removal efficiency of COD, turbidity and ammonium were 30.05%, 46.51% and 72.49%, respectively. Phosphate precipitation formation, hydroxide sinking formation, adsorption flocculation were the main way to remove inorganic pollutants. The removal mechanism of COD varied with pH, at 2.18 to 8 of pH, the removal of COD was mainly due to the formation of insoluble metal complexes, the electrical neutralization and the rewinding of the net, at 10 to 12 of pH, the main mechanism was adsorption of the hydroxide flocs and roll netting. The results can provide theoretical guidance for the application of the neutralization and precipitation process to treat coating wastewater.
Key words:coating wastewater/
neutralization and precipitation process/
heavy metal/
removal efficiency/
floc morphology/
reaction mechanisms.
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pH对中和沉淀法处理涂装废水效果影响及作用机理
付海娟1,2,,池勇志1,2,
赵建海1,2,
田秉晖3,
付翠莲1,4,
郑先强5
1.天津城建大学环境与市政工程学院天津市水质科学与技术重点实验室,天津 30038
2.天津城建大学基础设施防护和环境绿色生物技术国际联合研究中心,天津 30038
3.中国科学院生态环境研究中心环境水质学国家重点实验室,北京 10008
4.天津城建大学建筑设计研究院,天津 30038
5.天津天一爱拓科技有限公司,天津 30038
基金项目: 天津市科技计划项目(16YFXTSF00390) 天津市科技计划项目(15ZCZDSF00150) 天津城建大学科技成果转化奖励专项资金项目(KZZH2-A2-1726)
关键词: 涂装废水/
中和沉淀法/
重金属/
去除率/
絮体形貌/
反应机理
摘要:采用中和沉淀法对涂装废水进行处理,研究了pH(4~12)对废水中总磷、COD、浊度、总铁、总镍、总锰等12种主要污染物去除率的影响,并结合絮体粒度分布、Zeta电位、絮体形貌和XRD图谱等表征方式对COD和重金属的去除机理进行了分析。研究结果表明,在综合考虑后续生化处理需要和处理成本的条件下,中和沉淀法处理涂装废水的适宜pH为8,废水经处理后所有重金属离子浓度和总磷浓度均达到《污水排入城镇下水道水质标准》 (GB/T 31962-2015 )B级标准,COD、浊度和氨氮的去除率分别为30.05%、46.51%和72.49%。无机污染物去除的主要途径包括磷酸盐沉淀形成、氢氧化物沉淀形成和吸附絮凝作用。COD的去除机制随着pH的变化而不同,在pH =2.18~8时,COD的去除主要由于不溶性金属络合物的形成、电性中和与卷扫网捕,在pH =10~12时,主要的作用机制为氢氧化物絮体对其的吸附作用和卷扫网捕。这对中和沉淀法工艺处理实际涂装废水有重要的指导意义。
English Abstract
Mechanism and effect of pH on coating wastewater in neutralization and precipitation process
FU Haijuan1,2,,CHI Yongzhi1,2,
ZHAO Jianhai1,2,
TIAN Binghui3,
FU Cuilian1,4,
ZHENG Xianqiang5
1.Tianjin Key Laboratory of Water Quality Science and Technology, School of Environmental and Municipal Engineering, Tianjin Chengjian University, Tianjin 300384,Chin
2.Joint Research Centre for Protective Infrastructure Technology and Environmental Green Bioprocess, Tianjin Chengjian University, Tianjin 300384, Chin
3.State Key Laboratory of Environmental Aquatic Chemistry, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, Chin
4.Architectural Design and Research Institute, Tianjin Chengjian University, Tianjin 300384, Chin
5.Tianjin Tisun Itasca Technology Co.Ltd., Tianjin 300384, Chin
Keywords: coating wastewater/
neutralization and precipitation process/
heavy metal/
removal efficiency/
floc morphology/
reaction mechanisms
Abstract:The neutralization and precipitation process was used for coating wastewater treatment, the effects of pH (4 to 12) on the removal efficiencies of 12 major pollutants such as total phosphorus, COD, turbidity, total iron, total nickel and total manganese were studied and the removal mechanisms of COD and heavy metals were analyzed with the floc size distribution, Zeta potential, the morphology of flocs and XRD patterns. The results showed that suitable pH was 8 for treatment of coating wastewater by neutralization and precipitation process. After the wastewater was treated by the process, the concentration of all heavy metal ions and total phosphorus in the wastewater could meet the class B standard of Wastewater Quality of Standards for Discharge to Municipal Sewers (GB/T 31962-2015). At pH=8, the removal efficiency of COD, turbidity and ammonium were 30.05%, 46.51% and 72.49%, respectively. Phosphate precipitation formation, hydroxide sinking formation, adsorption flocculation were the main way to remove inorganic pollutants. The removal mechanism of COD varied with pH, at 2.18 to 8 of pH, the removal of COD was mainly due to the formation of insoluble metal complexes, the electrical neutralization and the rewinding of the net, at 10 to 12 of pH, the main mechanism was adsorption of the hydroxide flocs and roll netting. The results can provide theoretical guidance for the application of the neutralization and precipitation process to treat coating wastewater.