功能材料
功能材料
공능재료
JOURNAL OF FUNCTIONAL MATERIALS
2015年
9期
9081-9085,9091
,共6页
位子涵%孙永娇%赵振廷%梁燕飞%胡杰
位子涵%孫永嬌%趙振廷%樑燕飛%鬍傑
위자함%손영교%조진정%량연비%호걸
液相沉积法%ZnO%Mn掺杂%甲基橙%光催化降解
液相沉積法%ZnO%Mn摻雜%甲基橙%光催化降解
액상침적법%ZnO%Mn참잡%갑기등%광최화강해
liquid phase deposition%zinc oxide%Mn-doped%methyl orange%photocatalytic degradation
采用液相沉积法,在室温条件下制备了不同Mn掺杂浓度(0,0.25%,0.5%和1.0%(摩尔分数))的花状ZnO 微结构.利用X射线衍射(XRD)、扫描电子显微镜(SEM)和透射电子显微镜(TEM)对制备的花状ZnO 微结构的物相及形貌进行表征.以甲基橙溶液作为光催化反应模型污染物,对不同浓度的 Mn 掺杂花状ZnO 微结构的光催化性能进行了研究.实验结果表明,Mn在ZnO 材料中以两种形态存在,即进入晶格以Mn2+形式替代 Zn2+和以 Mn3 O4形式附着在ZnO 材料表面.且 Mn 掺杂提高了花状 ZnO 微球结构的光催化活性,当掺杂浓度为0.25%(摩尔分数)时光催化性能最优,紫外光照2.0 h 后,对甲基橙的光催化降解率可达88.7%.
採用液相沉積法,在室溫條件下製備瞭不同Mn摻雜濃度(0,0.25%,0.5%和1.0%(摩爾分數))的花狀ZnO 微結構.利用X射線衍射(XRD)、掃描電子顯微鏡(SEM)和透射電子顯微鏡(TEM)對製備的花狀ZnO 微結構的物相及形貌進行錶徵.以甲基橙溶液作為光催化反應模型汙染物,對不同濃度的 Mn 摻雜花狀ZnO 微結構的光催化性能進行瞭研究.實驗結果錶明,Mn在ZnO 材料中以兩種形態存在,即進入晶格以Mn2+形式替代 Zn2+和以 Mn3 O4形式附著在ZnO 材料錶麵.且 Mn 摻雜提高瞭花狀 ZnO 微毬結構的光催化活性,噹摻雜濃度為0.25%(摩爾分數)時光催化性能最優,紫外光照2.0 h 後,對甲基橙的光催化降解率可達88.7%.
채용액상침적법,재실온조건하제비료불동Mn참잡농도(0,0.25%,0.5%화1.0%(마이분수))적화상ZnO 미결구.이용X사선연사(XRD)、소묘전자현미경(SEM)화투사전자현미경(TEM)대제비적화상ZnO 미결구적물상급형모진행표정.이갑기등용액작위광최화반응모형오염물,대불동농도적 Mn 참잡화상ZnO 미결구적광최화성능진행료연구.실험결과표명,Mn재ZnO 재료중이량충형태존재,즉진입정격이Mn2+형식체대 Zn2+화이 Mn3 O4형식부착재ZnO 재료표면.차 Mn 참잡제고료화상 ZnO 미구결구적광최화활성,당참잡농도위0.25%(마이분수)시광최화성능최우,자외광조2.0 h 후,대갑기등적광최화강해솔가체88.7%.
In this paper,Mn-doped flower-like ZnO microstructures with various doping concentration (0,0.25, 0.5 and 1.0mol %)were fabricated using liquid phase deposition at room temperature.The phases and morphol-ogies of Mn-doped flower-like ZnO microstructures were characterized by XRD,SEM and TEM.The photocata-lytic performances of Mn-doped flower-like ZnO microstructures with various doping concentration were studied using methyl orange as the stimulant pollutant.The measured results indicated that Zn2+ maybe replaced by Mn2+ in the lattice of ZnO or exist on the surface of ZnO nanoplates as Mn3 O4 .Moreover,the experimental re-sults prove that Mn-doped ZnO microstructures can improve the performance of photocatalytic degradation.The optimization of Mn content is 0.25mol%,and degradation rate for methyl orange can reach to 88.7%.