高校化学工程学报
高校化學工程學報
고교화학공정학보
JOURNAL OF CHEMICAL ENGINEERING OF CHINESE UNIVERSITIES
2014年
3期
665-670
,共6页
李英芝%詹亚力%张华%吴百春
李英芝%詹亞力%張華%吳百春
리영지%첨아력%장화%오백춘
RO浓水%臭氧氧化%树脂吸附分离%三维荧光光谱%傅里叶红外光谱
RO濃水%臭氧氧化%樹脂吸附分離%三維熒光光譜%傅裏葉紅外光譜
RO농수%취양양화%수지흡부분리%삼유형광광보%부리협홍외광보
RO concentrate%ozone oxidation%resin adsorption separation%3D-EEM%FT-IR
采用XAD-8树脂对臭氧氧化前后炼厂反渗透(RO)浓水中的有机物进行组分分离,并采用紫外分光光度法(UV)、傅里叶红外光谱(FT-IR)、三维荧光光谱(3D-EEM)等方法对不同组分的结构进行表征。结果表明,RO浓水中含有大量的富里酸类腐殖质和腐殖酸类腐殖质等荧光物质;原水溶解性有机物(DOC)含量为(46.1±0.5) mg?L-1,其中疏水酸性有机物(HoA)、疏水碱性有机物(HoB)、疏水中性有机物(HoN)及亲水性物质(HiM)四种组分的比例分别为20.8%、4.5%、27.3%及47.5%。臭氧氧化后各组分比例分别为21.5%、2.6%、15.1%及60.6%,亲水性物质增加了13.1%,但DOC去除率仅为2.5%;HoA和HoN中大量含有C=C、C=O等不饱和键和芳香结构物质,而HiM中含量很少,但含有大量含C-O键及脂肪烃类物质;臭氧氧化可以降低RO浓水中有机物的芳香性构化程度,破坏其中难以被降解的不饱和键,使疏水性物质大量被氧化成亲水性物质。
採用XAD-8樹脂對臭氧氧化前後煉廠反滲透(RO)濃水中的有機物進行組分分離,併採用紫外分光光度法(UV)、傅裏葉紅外光譜(FT-IR)、三維熒光光譜(3D-EEM)等方法對不同組分的結構進行錶徵。結果錶明,RO濃水中含有大量的富裏痠類腐殖質和腐殖痠類腐殖質等熒光物質;原水溶解性有機物(DOC)含量為(46.1±0.5) mg?L-1,其中疏水痠性有機物(HoA)、疏水堿性有機物(HoB)、疏水中性有機物(HoN)及親水性物質(HiM)四種組分的比例分彆為20.8%、4.5%、27.3%及47.5%。臭氧氧化後各組分比例分彆為21.5%、2.6%、15.1%及60.6%,親水性物質增加瞭13.1%,但DOC去除率僅為2.5%;HoA和HoN中大量含有C=C、C=O等不飽和鍵和芳香結構物質,而HiM中含量很少,但含有大量含C-O鍵及脂肪烴類物質;臭氧氧化可以降低RO濃水中有機物的芳香性構化程度,破壞其中難以被降解的不飽和鍵,使疏水性物質大量被氧化成親水性物質。
채용XAD-8수지대취양양화전후련엄반삼투(RO)농수중적유궤물진행조분분리,병채용자외분광광도법(UV)、부리협홍외광보(FT-IR)、삼유형광광보(3D-EEM)등방법대불동조분적결구진행표정。결과표명,RO농수중함유대량적부리산류부식질화부식산류부식질등형광물질;원수용해성유궤물(DOC)함량위(46.1±0.5) mg?L-1,기중소수산성유궤물(HoA)、소수감성유궤물(HoB)、소수중성유궤물(HoN)급친수성물질(HiM)사충조분적비례분별위20.8%、4.5%、27.3%급47.5%。취양양화후각조분비례분별위21.5%、2.6%、15.1%급60.6%,친수성물질증가료13.1%,단DOC거제솔부위2.5%;HoA화HoN중대량함유C=C、C=O등불포화건화방향결구물질,이HiM중함량흔소,단함유대량함C-O건급지방경류물질;취양양화가이강저RO농수중유궤물적방향성구화정도,파배기중난이피강해적불포화건,사소수성물질대량피양화성친수성물질。
Before and after ozone oxidation, the dissolved organics (DOM) in reverse osmosis (RO) concentrates from oil refining were separatively separated by XAD-8 resins and characterized by ultraviolet spectrophotometry (UV254), fourier infrared spectroscopy (FT-IR) and three dimensional fluorescence spectroscopy (3D-EEM). The results show that humic-like and fulvic-like substances are found in the RO concentrates. Before ozone oxidation, the original dissolved organics (DOC) has a concentration of ( 46.1 ± 0.5) mg?L-1, which can be classified as drainage water acidic organics (HoA, 20.8%), hydrophobic basic organics (HoB, 4.5%), hydrophobic neutral organics (HoN, 27.3%) and hydrophilic substances (HiM, 47.5%). The concentrations of HoA、HoB、HoN and HiM become 21.5%、2.6%、15.1% and 60.6%, respectively after ozonation, while the concentration of hydrophilic substances increases by 13.1%. However, The DO removal ratio is about 2.5%. C=C, C=O and other unsaturated bond exist in HoA and HoN , and there are more C-O and aliphatic hydrocarbons in HiM. Aromatic structures and unsaturated bonds can be destroyed by ozonation treatment and a large number of hydrophobic substances are transformed into hydrophilic substances.