期刊文献+

八乙墓卟啉和四苯基卟啉合钌(Ⅱ)及锇(Ⅱ)的二氧加合物的红外光谱 被引量:4

INFRARED SPECTRA OF DIOXYGEN ADDUCTS OF RUTHENIUM(Ⅱ) AND OSMIUM(Ⅱ) OCTAETHYLPORPHINE AND TETRAPHENYLPORPHINE
下载PDF
导出
摘要 OEP(八乙基卟啉阴离子)和TPP(四苯基卟啉阴离子)合钌(Ⅱ)和锇(Ⅱ)的二氧加合物由matrix分离技术得到(T=20-43K,P=10-5-10-6torr).为了确定v(O2)带的归属应用了同位素取代法16O2/18O2.IR谱说明对于钌的两种加合物(指OEP和TPP)都有两种异构体,其V(16O2)频率为:Ru(OEP)O2,1141和1103cm-1;Ru(TPP)O2,1167和1114cm-1.Os(TPP)O2只生成一种异构体,v(16O2)=1090cm-1,异构体v(16O2):[Ru(OEP)O2],1141cm-1,[Ru(TPP)O2],1167cm-1,这些加合物约在100K时分解,它们的结构指定为endon,而异构体[Ru(OEP)O2],1103cm-1,[Ru(TPP)O2],1114cm-1和[Os(TPP)O2],1090cm-1,在240—270K分解,它们的结构指定为桥联二聚体.在加合物中,将OEP换成TPP引起的钌加合物v(O2)频率的改变比铁和钴加合物更大.v(O2)相对强度的变化顺序为:Fe(Ⅱ)→Ru(Ⅱ)→Os(Ⅱ). Dioxygen adducts of Ru(Ⅱ) and Os(Ⅱ) with OEP (octaethylporphyrinato anion) and TPP(tetraphenylporphyrinato anion) were obtained by using the matrix isolation technique (T=20-43K andP=10-5-10-5- 10-6 torr). To assign v(O2) bands the isotope substitution 16O2/ 18O2 has been applied. IRspectroscopy revealed that in the case of Ru adducts two isomers exist in both adducts for which v(16O2)band frequencics amount to 1141 and 1103cm-1 for Ru(OEP)O2; for Ru(TPP)O2 they are 1167 and11 14cm-1. Os(TPP)O2 forms one isomer only for which (16O2) = 1090cm-1. Isomers of v(16O2) frequencies:1141cm-1 [Ru(OEP)O2] and 1167cm-1 [Ru(TPP)O2] which decompose at ca 100K have been assigned theend-on structure, while isomers 1103cm-1 [Ru(OEP)O2], 1114cm-1 [Ru(TPP)O2] and1090cm-1 [Os(TPP)O2] that decompose at 240-270K the bridging dimer structure. Substitution of OEP byTPP in adducts causes more considerable changes in v(O2) band frequencies in case of Ru, as comparedwith Fe and Co.
出处 《无机化学学报》 SCIE CAS CSCD 北大核心 1994年第1期6-12,共7页 Chinese Journal of Inorganic Chemistry
关键词 八乙基卟啉 四苯基卟啉 络合物 dioxygen of Ru(Ⅱ) and Os(Ⅱ) porphyrin matrix isolation IR spectroscopy
  • 相关文献

参考文献1

  • 1Che C M,Inorg Chem,1988年,27卷,2801页 被引量:1

同被引文献27

  • 1郑伟.Fenton试剂特性及其在水处理中的应用[J].硅谷,2009,2(22). 被引量:1
  • 2盛涤伦,马凤娥.新型起爆药DACP的合成及其主要性能[J].含能材料,2006,14(3):161-164. 被引量:16
  • 3Guedes A,Madeira L M P,Boaven tura R A R,et al.Fenton oxidation of cork cooking wastewater-overall kinetic analysis. Water Research . 2003 被引量:1
  • 4Deng Y,Englehardt J D.Treatment of landfill leachate by Fenton process. Water Research . 2006 被引量:1
  • 5Zhang H,Choi H J,Huang C P.Optimization of Fenton process for treatment for the landfill leachate. Journal of Harzardous Matericls . 2005 被引量:1
  • 6Lucas M S,Peres J A.Removal of COD from olive mill wastewater by Fenton‘s reagent:Kinetics study. Journal of Hazardous Materials . 2009 被引量:1
  • 7Yun Whan Kang,Kyung-Yub Hwang.Effects of reaction conditions on the oxidation efficiency in the Fenton process. Water Research . 2000 被引量:1
  • 8Tang W,Tassos S.Oxidation kinetics and mechanismsof trihal-omethanes by Fenton reagent. Water Re-search . 被引量:1
  • 9Bossmann SH,Oliveros E,Gob S,et al.New evidence against hydroxyl radicals as reactive intermediates in the thermal and photochemically enhanced Fenton reaction. Journal of Physics . 1998 被引量:1
  • 10Huston PL,Pignatello JJ.Reduction of perchloroalkanes by ferrioxalate-generated carboxylat radical preceding mineralization by the photo-Fenton reation. Environmental Sciences . 1996 被引量:1

引证文献4

二级引证文献9

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部