| Lanthanide coordination polymers(Ln-CPs),especially Eu3+/Tb3+as metal nodes,not only have the advantages of high porosity,large specific surface area,open active site,adjustable pore size,and good thermal and chemical stability.Ln-CPs have the advantages of lanthanide ion sharp and characteristic emission,large Stokes shift,long fluorescence lifetime and high quantum yield.Ln-CPs have a unique luminescence process(energy transfer from organic ligand to Ln3+),and the interaction between analyte and Ln3+or analyte and ligand will affect the luminescence intensity of Ln-CPs.Due to the diversity of organic ligands,Ln-CPs showed a variety of responses to different analytes.Based on this,Ln-CPs can be used as fluorescent sensing materials for metal cations,anions,antibiotics,nitro explosives and pesticides.At the same time,Ln-CPs can be used as photocatalyst for photocatalytic degradation of tetracycline pollutants to achieve the purpose of pollutant removal.In this thesis,Eu3+and Tb3+are used as metal nodes.5-(pyridin-2-ylmethoxy)isophthalic acid(2-H2pyia)and 5-(pyridin-3-ylmethoxy)isophthalic acid(3-H2pyia)were carboxylic acid ligands,1,10-phenanthroline(phen),4,4’-Bipyridyl(4,4’-bipy),imidazo[4,5-f][1,10]phenanthroline(IDP),4,4’-bis(imidazol-1-ylmethyl)biphenyl(4,4’-bimp),2,2’-Bipyridyl(2,2’-bipy)were nitrogen-containing ligands.Eight kinds of Ln-CPs materials were successfully synthesized by hydrothermal method.[Tb2(2-pyia)3(phen)2(H2O)]·H2O(1),[Tb(2-pyia)(Ac)(IDP)](2),[Tb4(2-pyia)6(HAc)0.5(2,2’-bipy)(H2O)4.5]·(2,2’-bipy)·H2O(3),[Tb(2-pyia)(Ac)(H2O)](4)[Eu2(3-pyia)3(H2O)4]·(4,4’-bipy)·3H2O(5),[Eu2(3-pyia)2(Ac)2(H2O)4]·(2,2’-bipy)0.5·4.25H2O(6),[Eu(3-pyia)(Ac)(4,4’-bimp)](7)and[Eu(3-pyia)(Ac)(H2O)2]·H2O(8).Their structures were analyzed and characterized by elemental analysis,single crystal X-ray diffraction,infrared spectroscopy(IR),thermogravimetric analysis(TG)and XRD.Meanwhile,the fluorescence sensing and photocatalytic degradation properties of Ln-CPs were studied.1.Using Tb3+as metal node,2-H2pyia as carboxylic acid ligand,phen,2,2’-bipy,IDP as nitrogen-containing ligand,four kinds of Tb-CPs(1-4)were successfully synthesized under hydrothermal conditions.The structure analysis of CPs 1-4 shows that CPs 1,3 and 4 are two-dimensional network structure,and CP 2 is one-dimensional chain structure.Fluorescence sensing experiments showed that CPs 1-3 responded to fluorescence quenching of Fe3+,CPs 1 and 3 responded to fluorescence quenching of Cr2O72-,tetracycline,2,4,6-trinitrophenol,CPs 2 and 4 responded to fluorescence quenching of cefixime,CP 2 responded to fluorescence quenching of p-nitrophenol,CP 4responded to fluorescence quenching of nitrobenzene.Both CPs 1-4 responded to fluorescence quenching of fluridine.The mechanism of the fluorescence response of CPs1-4 to the analyte was discussed as competitive absorption,photoinduced electron transfer and dynamic/static quenching.2.Using Eu3+as metal node,3-H2pyia as carboxylic acid ligand,4,4’-bipy,2,2’-bipy and 4,4’-bimp as nitrogen-containing ligand,four kinds of Eu-CPs(5-8)were successfully synthesized under hydrothermal conditions.The structure analysis of CPs5-8 showed that CPs 5 and 7 were two-dimensional network structure,and CPs 6 and 8were one-dimensional chain structure.The fluorescence sensing experiments showed that CP 5 enhanced the fluorescence response of Cu2+,B4O72-,tetracycline and imidamine,and quenched the fluorescence response of pyrimethanil.CP 6 responded to enhanced fluorescence of Cu2+and imidamine,while nitrobenzene and pyrimethanil responded to fluorescence quenching.CP 7 responded to enhanced fluorescence of imidamine,and quenched fluorescence of ornidazole,nitrobenzene and fluridine.Response of CP 8 to fluorescence quenching of metronidazole,nitrobenzene and fluridine.The response mechanism of CPs 5-8 to the analyte was discussed.The fluorescence quenching mechanism may be a combination of competitive absorption,photoinduced electron transfer and dynamic/static quenching.The mechanism of fluorescence enhancement may be the combination of photoelectron transfer and weak interaction between analyte and ligand.3.The photocatalytic degradation performance on tetracycline of activated products of CPs 3 and 5 were studied.The photocatalytic degradation efficiency of CP 3 and its activated product were 84.29%and 96.07%,and the degradation efficiency of CP 5 and its activated product were 77.74%and 79.15%,respectively.The photocatalytic mechanism of the complexes and its activated products was also discussed.The results indicated that.O2-and h+were the main active species. |