中国环境科学
中國環境科學
중국배경과학
CHINA ENVIRONMENTAL SCIENCE
2009年
11期
1171-1176
,共6页
苏营营%于艳卿%杨沛珊%王新亭%朱校斌
囌營營%于豔卿%楊沛珊%王新亭%硃校斌
소영영%우염경%양패산%왕신정%주교빈
纳米TiO_2%硅藻土%复合物%光催化%弱酸性艳蓝RAW
納米TiO_2%硅藻土%複閤物%光催化%弱痠性豔藍RAW
납미TiO_2%규조토%복합물%광최화%약산성염람RAW
nano-TiO_2%diatomite%composite%photocatalytic%weak acid brilliant blue RAW
为提高光催化剂的稳定性,选取硅藻土为载体,以钛酸四异丙酯为前驱物,采用溶胶一凝胶法制备了TiO_2/硅藻土光催化剂,并利用XRD、SEM、FT-IR等技术对其进行表征.以蒽醌染料弱酸性艳蓝RAW为目标降解物,考察了TiO_2/硅藻土的光催化活性、最佳pH值范围及催化剂重复使用对光催化活性的影响.结果表明,所制备的TiO_2为锐钛矿和金红石混晶型,平均粒径11nm,通过控制硅藻土加入量可以得到负载均匀的光催化剂所制备的TiO_2/硅藻土具有较强的光催化活性,对弱酸性艳蓝RAW的降解效果好于商品Degussa P25型TiO_2,最佳pH值为4.0.该催化剂性质稳定,重复使用15次后,催化活性仅降低12.4%.
為提高光催化劑的穩定性,選取硅藻土為載體,以鈦痠四異丙酯為前驅物,採用溶膠一凝膠法製備瞭TiO_2/硅藻土光催化劑,併利用XRD、SEM、FT-IR等技術對其進行錶徵.以蒽醌染料弱痠性豔藍RAW為目標降解物,攷察瞭TiO_2/硅藻土的光催化活性、最佳pH值範圍及催化劑重複使用對光催化活性的影響.結果錶明,所製備的TiO_2為銳鈦礦和金紅石混晶型,平均粒徑11nm,通過控製硅藻土加入量可以得到負載均勻的光催化劑所製備的TiO_2/硅藻土具有較彊的光催化活性,對弱痠性豔藍RAW的降解效果好于商品Degussa P25型TiO_2,最佳pH值為4.0.該催化劑性質穩定,重複使用15次後,催化活性僅降低12.4%.
위제고광최화제적은정성,선취규조토위재체,이태산사이병지위전구물,채용용효일응효법제비료TiO_2/규조토광최화제,병이용XRD、SEM、FT-IR등기술대기진행표정.이은곤염료약산성염람RAW위목표강해물,고찰료TiO_2/규조토적광최화활성、최가pH치범위급최화제중복사용대광최화활성적영향.결과표명,소제비적TiO_2위예태광화금홍석혼정형,평균립경11nm,통과공제규조토가입량가이득도부재균균적광최화제소제비적TiO_2/규조토구유교강적광최화활성,대약산성염람RAW적강해효과호우상품Degussa P25형TiO_2,최가pH치위4.0.해최화제성질은정,중복사용15차후,최화활성부강저12.4%.
In order to improve the stability of photocatalyst, TiO_2/diatomite was prepared by sol-gel method with titanium (IV) isopropoxide as precursor, which was then characterized by XRD, SEM and FT-IR. The photocatalytic activity of the composite was determined using anthraquinone dye weak acid brilliant blue RAW as model pollutant. Influences of solution pH and the photocatalyst-reused on photocatalytic activity were also investigated. TiO_2 coated on the surface of diatomite showed mixed crystal of anatase and rutile with an average particle size of 11 nm. The uniform TiO_2 coating could be achieved by controlling the amount of added diatomite. The TiO_2/diatomite demonstrated strong photocatalytic activity, and the decolorizing rate for weak acid brilliant blue RAW solution was higher than that for the Degussa P25-TiO_2. The optimum pH for photocatalytic reaction was 4.0. The TiCVdiatomite also showed strong stability, with its photocatalytic activity reducing only 12.4% after repeated use for 15 times.