华南师范大学学报(自然科学版)
華南師範大學學報(自然科學版)
화남사범대학학보(자연과학판)
JOURNAL OF SOUTH CHINA NORMAL UNIVERSITY (NATURAL SCIENCE EDITION)
2014年
2期
61-66
,共6页
直接沉淀合成%纳米SnO2%亚甲基蓝%光催化降解
直接沉澱閤成%納米SnO2%亞甲基藍%光催化降解
직접침정합성%납미SnO2%아갑기람%광최화강해
direct precipitation synthesis%nano-SnO2%methylene blue%photocatalytic degradation
采用四氯化锡与氢氧化钠在92℃下直接沉淀法制备了纳米级SnO2,经不同温度处理得到性质不同的SnO2样品.研究了处理温度对SnO2性质和紫外光(254 nm)照射下降解亚甲基蓝(MB)效率的影响.结果显示:200℃处理样品的降解率最高,超过该温度后,随着处理温度的升高,SnO2的粒径逐渐增大,比表面依次减小,表面吸附的羟基或水的数量减少,则样品的降解率逐渐减小.SnO2降解MB的反应为拟一级反应,满足Langmuir-Hinshelwood 模型,且在UV/SnO2降解体系中,羟自由基OH·为主要的活性体,它与MB反应导致其最终分解为CO2、H2 O和无机酸根离子等无害物质.
採用四氯化錫與氫氧化鈉在92℃下直接沉澱法製備瞭納米級SnO2,經不同溫度處理得到性質不同的SnO2樣品.研究瞭處理溫度對SnO2性質和紫外光(254 nm)照射下降解亞甲基藍(MB)效率的影響.結果顯示:200℃處理樣品的降解率最高,超過該溫度後,隨著處理溫度的升高,SnO2的粒徑逐漸增大,比錶麵依次減小,錶麵吸附的羥基或水的數量減少,則樣品的降解率逐漸減小.SnO2降解MB的反應為擬一級反應,滿足Langmuir-Hinshelwood 模型,且在UV/SnO2降解體繫中,羥自由基OH·為主要的活性體,它與MB反應導緻其最終分解為CO2、H2 O和無機痠根離子等無害物質.
채용사록화석여경양화납재92℃하직접침정법제비료납미급SnO2,경불동온도처리득도성질불동적SnO2양품.연구료처리온도대SnO2성질화자외광(254 nm)조사하강해아갑기람(MB)효솔적영향.결과현시:200℃처리양품적강해솔최고,초과해온도후,수착처리온도적승고,SnO2적립경축점증대,비표면의차감소,표면흡부적간기혹수적수량감소,칙양품적강해솔축점감소.SnO2강해MB적반응위의일급반응,만족Langmuir-Hinshelwood 모형,차재UV/SnO2강해체계중,간자유기OH·위주요적활성체,타여MB반응도치기최종분해위CO2、H2 O화무궤산근리자등무해물질.
The nano-SnO2 was synthesized by direct precipitation of tin tetrachloride ( SnCl4 ) and sodium hydroxide ( NaOH) at 92 ℃and a series of SnO 2 samples with different characters were obtained by calcined at different tem-peratures .The effects of calcination temperature on characters of SnO 2 and photodegradation of methylene blue ( MB) under UV-light (254 nm) irradiation have been investigated .The SnO2 sample calcined at 200 ℃showed the highest MB degradation rate .When the calcination temperature is over 200℃, with increasing calcination tem-perature the particle size of SnO 2 increases and the specific area of SnO 2 decreased , so the degradation rates of MB are decreased .The photocatalytic degradation kinetics was analyzed in detail , which fits a pseudo-first-order kinet-ics and the Langmuir-Hinshelwood model .In UV/SnO2 system the hydroxyl radical OH · play a critical role in the degradation of MB , inducing the complete mineralization of MB to carbon dioxide , water and mineral acid .