期刊文献+

Impacts of Power Density on Heavy Metal Release During Ultrasonic Sludge Treatment Process

超声波污泥处理过程中声能密度对重金属释放的影响(英文)
下载PDF
导出
摘要 The impact of ultrasonic power density on changes of heavy metals during sludge sonication was inves-tigated. Results showed that ultrasound could release heavy metals from sludge into the supernatant. There existed an effective power density range of 0.8-1.6 W·ml?1 for the release of the total heavy metal; there was little release below 0.8 W·ml?1 and too high power density was adverse to the release. Furthermore, sonication showed selective release of heavy metal from sludge to the supernatant; copper, cadmium and lead were not released by sonication, while arsenic and nickel were released easily and their release ratio could reach 40%. The effective energy range for each heavy metal was also different that 0.8-1.2 W·ml?1 for arsenic, 0.5-1.6 W·ml?1 for nickel, and 0.8-1.6 W·ml?1 for mercury and chrome. The differences among heavy metal release during sonication might be explained by the different distribution of chemical fractions of each metal in sludge. Such selectivity could be used to control heavy metal release during sludge treatment. The impact of ultrasonic power density on changes of heavy metals during sludge sonication was inves-tigated. Results showed that ultrasound could release heavy metals from sludge into the supernatant. There existed an effective power density range of 0.8-1.6 W·ml^-1 for the release of the total heavy metal;there was little release below 0.8 W·ml^-1 and too high power density was adverse to the release. Furthermore, sonication showed selective release of heavy metal from sludge to the supernatant;copper, cadmium and lead were not released by sonication, while arsenic and nickel were released easily and their release ratio could reach 40%. The effective energy range for each heavy metal was also different that 0.8-1.2 W·ml^-1 for arsenic, 0.5-1.6 W·ml^-1 for nickel, and 0.8-1.6 W·ml^-1 for mercury and chrome. The differences among heavy metal release during sonication might be explained by the different distribution of chemical fractions of each metal in sludge. Such selectivity could be used to control heavy metal release during sludge treatment.
出处 《Chinese Journal of Chemical Engineering》 SCIE EI CAS CSCD 2014年第4期469-473,共5页 中国化学工程学报(英文版)
基金 Supported by the Basic Research Funds in Renmin University of China from the center government(12XNL101)
关键词 activated sludge sonication METALS power density chemical fractions 污泥处理工艺 重金属释放 功率密度 超声波 超声处理 重金属污泥 密度范围 输出功率
  • 相关文献

参考文献1

二级参考文献30

  • 1Kern-Jespersen,J.P.,Henze,M.,"Biological phosphorus uptake under anoxic and aerobic conditions",Water Res.,27,617-624 (1993).
  • 2Meganck,M.,Faup,G.,"Enhanced biological phosphorus removal from wastewaters",In:Biotreatment Systems,Vol Ⅲ,Wise,D.,Ed.,CRC Press (1987).
  • 3Neyens,E.,Baeyens,J.,Weemaes,M.,De heyder,B.,"Advanced bio-solids treatment using H2O2-oxidation,Environ.Eng.Sci.,19,27-35 (2002).
  • 4Neyens,E.,Baeyens,J.,Weemaes,M.,De heyder,B.,"A review of thermal sludge pre-treatment processes to improve dewatering",J.Hazard.Mater.,98,51-67(2003).
  • 5Neyens,E.,Baeyens,J.,Weemaes,M.,De Heyder,B.,"Hot acid hydrolysis as a potential treatment of thickened sewage sludge",J.Hazard.Mater.,98,275-294(2003).
  • 6Dewil,R.,Baeyens,J.,Neyens,E.,"Fenton peroxidation improves the drying performance of waste activated sludge",J.Hazard.Mater.,106,161-170 (2004).
  • 7Qasim,S.R.,Wastewater Treatment Plants,2nd.ed.,Technomic Publ.Cy.,Lancaster,698-722 (1999).
  • 8Tran,F.T.,Tyagi,R.D.,"Mesophilic and thermophilic digestion of municipal sewage sludge in a deep U-shaped reactor",Water Sci.Technol.,22,205-215 (1990).
  • 9Tiehm,A.,Nickel,K.,Neis,U.,"The use of ultrasound to accelerate the anaerobic digestion of sewage sludge",Water Sci.Technol.,36,121-128 (1997).
  • 10Baeyens,J.,Canvain,B.,"Het bulking-verschijnsel",Procestechnieken en-engineering,35,17-35 (2000).(in Dutch)

共引文献20

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部