期刊文献+

Multiple transformation pathways of p-arsanilic acid to inorganic arsenic species in water during UV disinfection 被引量:4

Multiple transformation pathways of p-arsanilic acid to inorganic arsenic species in water during UV disinfection
原文传递
导出
摘要 p-Arsanilic acid(p-ASA) is widely used in China as livestock and poultry feed additive for promoting animal growth.The use of organoarsenics poses a potential threat to the environment because it is mostly excreted by animals in its original form and can be transformed by UV–Vis light excitation.This work examined the initial rate and efficiency of p-ASA phototransformation under UV-C disinfection lamp.Several factors influencing p-ASA phototransformation,namely,p H,initial concentration,temperature,as well as the presence of Na Cl,NH4+,and humic acid,were investigated.Quenching experiments and LC–MS were performed to investigate the mechanism of p-ASA phototransformation.Results show that p-ASA was decomposed to inorganic arsenic(including As(Ⅲ) and As(V))and aromatic products by UV-C light through direct photolysis and indirect oxidation.The oxidation efficency of p-ASA by direct photosis was about 32%,and those by HOU and1O2 were 19% and 49%,respectively.Cleavage of the arsenic–benzene bond through direct photolysis,HOU oxidation or1O2 oxidation results in simultaneous formation of inorganic As(Ⅲ),As(IV),and As(V).Inorganic As(Ⅲ) is oxidized to As(IV) and then to As(V) by1O2 or HOU.As(IV) can undergo dismutation or simply react with oxygen to produce As(V) as well.Reactions of the organic moieties of p-ASA produce aniline,aminophenol and azobenzene derivatives as main products.The photoconvertible property of p-ASA implies that UV disinfection of wastewaters from poultry and swine farms containing p-ASA poses a potential threat to the ecosystem,especially agricultural environments. p-Arsanilic acid(p-ASA) is widely used in China as livestock and poultry feed additive for promoting animal growth.The use of organoarsenics poses a potential threat to the environment because it is mostly excreted by animals in its original form and can be transformed by UV–Vis light excitation.This work examined the initial rate and efficiency of p-ASA phototransformation under UV-C disinfection lamp.Several factors influencing p-ASA phototransformation,namely,p H,initial concentration,temperature,as well as the presence of Na Cl,NH4+,and humic acid,were investigated.Quenching experiments and LC–MS were performed to investigate the mechanism of p-ASA phototransformation.Results show that p-ASA was decomposed to inorganic arsenic(including As(Ⅲ) and As(V))and aromatic products by UV-C light through direct photolysis and indirect oxidation.The oxidation efficency of p-ASA by direct photosis was about 32%,and those by HOU and1O2 were 19% and 49%,respectively.Cleavage of the arsenic–benzene bond through direct photolysis,HOU oxidation or1O2 oxidation results in simultaneous formation of inorganic As(Ⅲ),As(IV),and As(V).Inorganic As(Ⅲ) is oxidized to As(IV) and then to As(V) by1O2 or HOU.As(IV) can undergo dismutation or simply react with oxygen to produce As(V) as well.Reactions of the organic moieties of p-ASA produce aniline,aminophenol and azobenzene derivatives as main products.The photoconvertible property of p-ASA implies that UV disinfection of wastewaters from poultry and swine farms containing p-ASA poses a potential threat to the ecosystem,especially agricultural environments.
出处 《Journal of Environmental Sciences》 SCIE EI CAS CSCD 2016年第9期39-48,共10页 环境科学学报(英文版)
基金 supported by the National Natural Science Foundation of China(Nos 51508423 and 21477090)
关键词 p-Arsanilic acid Phototransformation Inorganic arsenic species Kinetics Mechanism p-Arsanilic acid Phototransformation Inorganic arsenic species Kinetics Mechanism
  • 相关文献

参考文献1

二级参考文献17

  • 1Belzile N,Chen Y W,Xu R R,2000.Early diagenetic behavior of selenium in freshwater sediments[J].Applied Geochemistry,15:1439-1454.
  • 2Burguera M,Burguer J L,1997.Analytical methodology for speciation of arsenic in environmental and biological samples[J].Talanta,44:1581-1604.
  • 3Cai Y,2000.Speciation and analysis of mercury,arsenic,and selenium by atomic fluorescence spectrometry[J].Trends in Analytical Chemistry,19:62-66.
  • 4Carignan R,Rapin F,Tessier T,1985.Sediment porewater sampling for metal analysis:a comparison of techniques[J].Geochimica et Cosmochimica Acta,49:2493-2497.
  • 5Chen Y W,Deng T L,Filella M et al.,2003.Distribution and early diagenesis of antimony species in sediments and porewater of freshwater lakes[J].Environmental Science and Technology,37:1163-1168.
  • 6Deng T L,Chen Y W,Belzile N,2001.Antimony speciation at ultra levels using hydride generation atomic fluorescence spectrometry and 8-hydroxyquinoline as an efficient masking agent[J].Analytica Chimica Acta,432:293-302.
  • 7Gong Z,Lu X,Ma M et al.,2002.Arsenic speciation analysis[J].Talanta,58:77-96.
  • 8Huang J H,Ilgen G,2004.Blank values,adsorption,pre-concentration,and sample preservation for arsenic speciation of environmental water samples[J].Analytica Chimica Acta,512:1-10.
  • 9Pantsar-Kallio M,Korpela A,2000.Analysis of gaseous arsenic species and stability studies of arsine and trimethylarsine by gas chromatography-mass spectrometry[J].Analytical Chimica Acta,410:65-70.
  • 10Pantsar-Kallio M,Manninen P K G,1997.Simultaneous determination of toxic arsenic and chromium species in water samples by ion chromatography-inductively coupled plasma mass spectrometry[J].Journal of Chromatography A,799:139-146.

共引文献11

同被引文献27

引证文献4

二级引证文献9

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