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研究了地下水环境条件下(低温、避光、特征离子共存等),金霉素在二氧化锰和铁锰复合氧化物上的降解行为.探讨了降解动力学以及pH条件、离子种类和强度等环境因素对降解的影响,并通过降解反应前后材料的变化,初步探索其降解机理.一级动力学方程能较好地拟合降解过程,铁锰复合氧化物的降解速率常数高于二氧化锰;外源阳离子K+、Na+、Ca2+、Mg2+对降解无显著影响,但阴离子HCO3-对降解有明显抑制.采用红外光谱对降解前后材料进行表征,发现二氧化锰上的Mn—OH和铁锰复合氧化物上的Fe—OH、Mn—O和Fe—O—Mn振动吸收峰在降解后明显减弱,表明这些可能为降解金霉素的活性位点,降解后材料能谱图上N、Cl元素的存在也同样证明金霉素在材料表面发生了氧化反应.

The degradation behaviors of chlortetracycline by iron and manganese oxides were studied under simulated groundwater environment (low temperature,dark and typical coexisting ions).The degradation kinetics and factors such as pH,species and dosages of ions,were investigated.And the degradation mechanisms were discussed through the changes of oxide materials before and after use.First-order reaction kinetic equation fitted the degradation processes of chlortetracycline by two oxides and the kinetic constants of the degradation by Fe-Mn bimetal oxides were generally higher than that by manganese dioxide.The coexisting HCO3-showed inhibition on the degradation efficiency of chlortetracycline,whereas cations exhibited no influence on it.Fourier transform infrared (FTIR) spectra showed that the vibration absorption intensities of Mn—OH in manganese dioxide,Fe—OH,Mn—O,and Fe—O—Mn in Fe-Mn bimetal oxides decreased,which suggested that they might be the active sites points.The existences of N and Cl elements on the used oxide materials,demonstrated by scanning electron microscope-energy dispersive spectrometer (SEM-EDS),also proved the oxidation reaction of chlortetracycline on the material surface.

参考文献

[1] Lei Tong;Ping Li;Yanxin Wang;Kuanzheng Zhu.Analysis Of Veterinary Antibiotic Residues In Swine Wastewater And Environmental Water Samples Using Optimized Spe-lc/ms/ms[J].Chemosphere: Environmental toxicology and risk assessment,20098(8):1090-1097.
[2] Davide Calamari;Ettore Zuccato;Sara Castiglioni;Renzo Bagnati;Roberto Fanelli.Strategic survey of therapeutic drugs in the rivers Po and Lambro in northern Italy[J].Environmental Science & Technology: ES&T,20037(7):1241-1248.
[3] Xiangang Hu;Qixing Zhou;Yi Luo.Occurrence and source analysis of typical veterinary antibiotics in manure, soil, vegetables and groundwater from organic vegetable bases, northern China[J].Environmental Pollution,20109(9):2992-2998.
[4] 张慧敏;章明奎;顾国平.浙北地区畜禽粪便和农田土壤中四环素类抗生素残留[J].生态与农村环境学报,2008(3):69-73.
[5] Elena Martínez-Carballo;Carmen González-Barreiro;Sigrid Scharf;Oliver Gans.Environmental monitoring study of selected veterinary antibiotics in animal manure and soils in Austria[J].Environmental Pollution,20072(2):570-579.
[6] 魏瑞成;葛峰;陈明;黄思瑜;王冉.江苏省畜禽养殖场水环境中四环类抗生素污染研究[J].农业环境科学学报,2010(6):1205-1210.
[7] Tuan Xuan Le;Yukihiro Munekage;Shin-ichiro Kato.Antibiotic resistance in bacteria from shrimp farming in mangrove areas[J].Science of the Total Environment,20051/3(1/3):95-105.
[8] 陈秋颖;金彩霞;吕山花;樊颖伦.兽药残留及其对生态环境影响的研究进展[J].安徽农业科学,2008(16):6943-6945,6952.
[9] 林志荣 .铁锰氧化物降解多氯联苯的研究[D].南京信息工程大学,2011.
[10] Huichun Zhang;Ching-Hua Huang.Oxidative transformation of triclosan and chlorophene by manganese oxides[J].Environmental Science & Technology: ES&T,200311(11):2421-2430.
[11] Hui Li;Linda S. Lee;Darrell G. Schulze;Christopher A. Guest.Role of soil manganese in the oxidation of aromatic amines[J].Environmental Science & Technology: ES&T,200312(12):2686-2693.
[12] K.A.BARRETT;M.B.MCBRIDE.Oxidative Degradation of Glyphosate and Aminomethylphosphonate by Manganese Oxide[J].Environmental Science & Technology: ES&T,200523(23):9223-9228.
[13] 陈高;赵玲;董元华.二氧化锰氧化降解金霉素的动力学研究[J].环境科学,2009(09):2773-2778.
[14] Gao Chen;Ling Zhao;Yuan-hua Dong.Oxidative degradation kinetics and products of chlortetracycline by manganese dioxide[J].Journal of hazardous materials,2011:128-138.
[15] Xu, W.;Wang, H.;Liu, R.;Zhao, X.;Qu, J..The mechanism of antimony(III) removal and its reactions on the surfaces of Fe-Mn Binary Oxide[J].Journal of Colloid and Interface Science,20111(1):320-326.
[16] 刘锐平;杨艳玲;夏圣骥;何文杰;韩宏大;李圭白.水合二氧化锰界面特性及其除污染效能[J].环境化学,2005(3):338-341.
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