环境科学与技术
環境科學與技術
배경과학여기술
ENVIRONMENTAL SCIENCE & TECHNOLOGY
2010年
4期
150-153,175
,共5页
刘娟%周许林%刘红%李扬薇%范先媛
劉娟%週許林%劉紅%李颺薇%範先媛
류연%주허림%류홍%리양미%범선원
酸性大红%氧化-絮凝耦合%高锰酸钾%聚硅硫酸钛
痠性大紅%氧化-絮凝耦閤%高錳痠鉀%聚硅硫痠鈦
산성대홍%양화-서응우합%고맹산갑%취규류산태
acid brilliant scarlet GR%potassium permanganate%coupled flocculation and oxidation%poly-titanic-silicic sulfate
选取浓度为25mg/L的酸性大红-GR溶液为模拟染料废水,采用氧化-絮凝耦合工艺,探索了氧化剂种类、絮凝剂种类、废水pH值、氧化剂和絮凝剂投加量对氧化-絮凝耦合处理酸性大红染料的影响,确定最佳处理条件为:酸性大红溶液初始pH值不变,高锰酸钾和PTSS的投加量分别为为20mg/L和10mg/L(以钛离子计),脱色率和COD去除率均最大,分别为96.3%、56.5%.通过FTIR光谱扫描、絮体的显微形貌观察、酸性大红和新型絮凝剂聚硅硫酸钛(PTSS)的表面电动电位随pH值的变化的测定,分析了氧化-絮凝耦合法的反应历程:高锰酸钾破坏酸性大红的发色基团后,自身被还原成新生态二氧化锰胶体;二氧化锰胶体吸附酸性大红及其氧化产物,并被无机高分子絮凝剂PTSS通过电中和及架桥网捕等作用卷裹成絮体.
選取濃度為25mg/L的痠性大紅-GR溶液為模擬染料廢水,採用氧化-絮凝耦閤工藝,探索瞭氧化劑種類、絮凝劑種類、廢水pH值、氧化劑和絮凝劑投加量對氧化-絮凝耦閤處理痠性大紅染料的影響,確定最佳處理條件為:痠性大紅溶液初始pH值不變,高錳痠鉀和PTSS的投加量分彆為為20mg/L和10mg/L(以鈦離子計),脫色率和COD去除率均最大,分彆為96.3%、56.5%.通過FTIR光譜掃描、絮體的顯微形貌觀察、痠性大紅和新型絮凝劑聚硅硫痠鈦(PTSS)的錶麵電動電位隨pH值的變化的測定,分析瞭氧化-絮凝耦閤法的反應歷程:高錳痠鉀破壞痠性大紅的髮色基糰後,自身被還原成新生態二氧化錳膠體;二氧化錳膠體吸附痠性大紅及其氧化產物,併被無機高分子絮凝劑PTSS通過電中和及架橋網捕等作用捲裹成絮體.
선취농도위25mg/L적산성대홍-GR용액위모의염료폐수,채용양화-서응우합공예,탐색료양화제충류、서응제충류、폐수pH치、양화제화서응제투가량대양화-서응우합처리산성대홍염료적영향,학정최가처리조건위:산성대홍용액초시pH치불변,고맹산갑화PTSS적투가량분별위위20mg/L화10mg/L(이태리자계),탈색솔화COD거제솔균최대,분별위96.3%、56.5%.통과FTIR광보소묘、서체적현미형모관찰、산성대홍화신형서응제취규류산태(PTSS)적표면전동전위수pH치적변화적측정,분석료양화-서응우합법적반응역정:고맹산갑파배산성대홍적발색기단후,자신피환원성신생태이양화맹효체;이양화맹효체흡부산성대홍급기양화산물,병피무궤고분자서응제PTSS통과전중화급가교망포등작용권과성서체.
Dyestuff waste water which is simulated by Acid Scarlet GR (25mg/L) was treated by coupled flocculation and oxidation process. The influence of oxidant species, flocculant species, waste water pH value, dosage of oxidant and flocculant was investigated, then the optimal operating conditions were determined, adding 20mg/L potassium permanganate and 10mg/L PTSS when the initial pH value of Acid Scarlet GR is unchanged, treatment effect is optimization and, the color and COD removal rates reached 96.3% and 56.5%. The reaction mechanism of coupled flocculation and oxidation process were also studied through infrared adsorption spectrum, morphology of aggregates, particle size distribution of flocculant, zeta potential of wastewater and poly-titanic-silicic sulfate. Results show that acid brilliant scarlet GR is oxidized into small organic molecules by potassium permanganate, then small organic molecules are adsorbed by the reduction product-newly formed hydrous manganese dioxide, which is enwrapped by charge neutralization and adsorption bridging action of poly-titanic-silicic sulfate in the next step.